occuCOP | R Documentation |
This function fits a single season occupancy model using count data.
occuCOP(data,
psiformula = ~1, lambdaformula = ~1,
psistarts, lambdastarts, starts,
method = "BFGS", se = TRUE,
engine = c("C", "R"), na.rm = TRUE,
return.negloglik = NULL, L1 = FALSE, ...)
data |
An |
psiformula |
Formula describing the occupancy covariates. |
lambdaformula |
Formula describing the detection covariates. |
psistarts |
Vector of starting values for likelihood maximisation with |
lambdastarts |
Vector of starting values for likelihood maximisation with |
starts |
Vector of starting values for likelihood maximisation with |
method |
Optimisation method used by |
se |
Logical specifying whether to compute ( |
engine |
Code to use for optimisation. Either |
na.rm |
Logical specifying whether to fit the model ( |
return.negloglik |
A list of vectors of parameters ( |
L1 |
Logical specifying whether the length of observations ( |
... |
Additional arguments to pass to |
See unmarkedFrameOccuCOP
for a description of how to supply data to the data
argument. See unmarkedFrame
for a more general documentation of unmarkedFrame
objects for the different models implemented in unmarked.
occuCOP
fits a single season occupancy model using count data, as described in Pautrel et al. (2023).
The occupancy sub-model is:
z_i \sim \text{Bernoulli}(\psi_i)
With z_i
the occupany state of site i
. z_i=1
if site i
is occupied by the species, i.e. if the species is present in site i
. z_i=0
if site i
is not occupied.
With \psi_i
the occupancy probability of site i
.
The observation sub-model is:
N_{ij} | z_i = 1 \sim \text{Poisson}(\lambda_{ij} L_{ij}) \\
N_{ij} | z_i = 0 \sim 0
With N_{ij}
the count of detection events in site i
during observation j
.
With \lambda_{ij}
the detection rate in site i
during observation j
(for example, 1 detection per day.).
With L_{ij}
the length of observation j
in site i
(for example, 7 days.).
What we call "observation" (j
) here can be a sampling occasion, a transect, a discretised session. Consequently, the unit of \lambda_{ij}
and L_{ij}
can be either a time-unit (day, hour, ...) or a space-unit (kilometer, meter, ...).
\psi
and \lambda
In order to perform unconstrained optimisation, parameters are transformed.
The occupancy probability (\psi
) is transformed with the logit function (psi_transformed = qlogis(psi)
). It can be back-transformed with the "inverse logit" function (psi = plogis(psi_transformed)
).
The detection rate (\lambda
) is transformed with the log function (lambda_transformed = log(lambda)
). It can be back-transformed with the exponential function (lambda = exp(lambda_transformed)
).
unmarkedFitOccuCOP
object describing the model fit. See the unmarkedFit
classes.
Léa Pautrel
Pautrel, L., Moulherat, S., Gimenez, O. & Etienne, M.-P. Submitted. Analysing biodiversity observation data collected in continuous time: Should we use discrete or continuous-time occupancy models? Preprint at \Sexpr[results=rd]{tools:::Rd_expr_doi("10.1101/2023.11.17.567350")}.
unmarked
,
unmarkedFrameOccuCOP
,
unmarkedFit-class
set.seed(123)
options(max.print = 50)
# We simulate data in 100 sites with 3 observations of 7 days per site.
nSites <- 100
nObs <- 3
# For an occupancy covariate, we associate each site to a land-use category.
landuse <- sample(factor(c("Forest", "Grassland", "City"), ordered = TRUE),
size = nSites, replace = TRUE)
simul_psi <- ifelse(landuse == "Forest", 0.8,
ifelse(landuse == "Grassland", 0.4, 0.1))
z <- rbinom(n = nSites, size = 1, prob = simul_psi)
# For a detection covariate, we create a fake wind variable.
wind <- matrix(rexp(n = nSites * nObs), nrow = nSites, ncol = nObs)
simul_lambda <- wind / 5
L = matrix(7, nrow = nSites, ncol = nObs)
# We now simulate count detection data
y <- matrix(rpois(n = nSites * nObs, lambda = simul_lambda * L),
nrow = nSites, ncol = nObs) * z
# We create our unmarkedFrameOccuCOP object
umf <- unmarkedFrameOccuCOP(
y = y,
L = L,
siteCovs = data.frame("landuse" = landuse),
obsCovs = list("wind" = wind)
)
print(umf)
# We fit our model without covariates
fitNull <- occuCOP(data = umf)
print(fitNull)
# We fit our model with covariates
fitCov <- occuCOP(data = umf, psiformula = ~ landuse, lambdaformula = ~ wind)
print(fitCov)
# We back-transform the parameter's estimates
## Back-transformed occupancy probability with no covariates
backTransform(fitNull, "psi")
## Back-transformed occupancy probability depending on habitat use
predict(fitCov,
"psi",
newdata = data.frame("landuse" = c("Forest", "Grassland", "City")),
appendData = TRUE)
## Back-transformed detection rate with no covariates
backTransform(fitNull, "lambda")
## Back-transformed detection rate depending on wind
predict(fitCov,
"lambda",
appendData = TRUE)
## This is not easily readable. We can show the results in a clearer way, by:
## - adding the site and observation
## - printing only the wind covariate used to get the predicted lambda
cbind(
data.frame(
"site" = rep(1:nSites, each = nObs),
"observation" = rep(1:nObs, times = nSites),
"wind" = getData(fitCov)@obsCovs
),
predict(fitCov, "lambda", appendData = FALSE)
)
# We can choose the initial parameters when fitting our model.
# For psi, intituively, the initial value can be the proportion of sites
# in which we have observations.
(psi_init <- mean(rowSums(y) > 0))
# For lambda, the initial value can be the mean count of detection events
# in sites in which there was at least one observation.
(lambda_init <- mean(y[rowSums(y) > 0, ]))
# We have to transform them.
occuCOP(
data = umf,
psiformula = ~ 1,
lambdaformula = ~ 1,
psistarts = qlogis(psi_init),
lambdastarts = log(lambda_init)
)
# If we have covariates, we need to have the right length for the start vectors.
# psi ~ landuse --> 3 param to estimate: Intercept, landuseForest, landuseGrassland
# lambda ~ wind --> 2 param to estimate: Intercept, wind
occuCOP(
data = umf,
psiformula = ~ landuse,
lambdaformula = ~ wind,
psistarts = rep(qlogis(psi_init), 3),
lambdastarts = rep(log(lambda_init), 2)
)
# And with covariates, we could have chosen better initial values, such as the
# proportion of sites in which we have observations per land-use category.
(psi_init_covs <- c(
"City" = mean(rowSums(y[landuse == "City", ]) > 0),
"Forest" = mean(rowSums(y[landuse == "Forest", ]) > 0),
"Grassland" = mean(rowSums(y[landuse == "Grassland", ]) > 0)
))
occuCOP(
data = umf,
psiformula = ~ landuse,
lambdaformula = ~ wind,
psistarts = qlogis(psi_init_covs))
# We can fit our model with a different optimisation algorithm.
occuCOP(data = umf, method = "Nelder-Mead")
# We can run our model with a C++ or with a R likelihood function.
## They give the same result.
occuCOP(data = umf, engine = "C", psistarts = 0, lambdastarts = 0)
occuCOP(data = umf, engine = "R", psistarts = 0, lambdastarts = 0)
## The C++ (the default) is faster.
system.time(occuCOP(data = umf, engine = "C", psistarts = 0, lambdastarts = 0))
system.time(occuCOP(data = umf, engine = "R", psistarts = 0, lambdastarts = 0))
## However, if you want to understand how the likelihood is calculated,
## you can easily access the R likelihood function.
print(occuCOP(data = umf, engine = "R", psistarts = 0, lambdastarts = 0)@nllFun)
# Finally, if you do not want to fit your model but only get the likelihood,
# you can get the negative log-likelihood for a given set of parameters.
occuCOP(data = umf, return.negloglik = list(
c("psi" = qlogis(0.25), "lambda" = log(2)),
c("psi" = qlogis(0.5), "lambda" = log(1)),
c("psi" = qlogis(0.75), "lambda" = log(0.5))
))
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