ct_fit_ds
fits detection functions to camera trap distance sampling data and estimates
animal density or abundance using bootstrap variance estimation. Supports both
single model fitting and automated model selection procedures.
Usage
ct_fit_ds(
data,
estimate = c("density", "abundance"),
cutpoints = NULL,
truncation = set_truncation(data = data, cutpoints = cutpoints),
formula = ~1,
key = c("hn", "hr", "unif"),
adjustment = c("cos", "herm", "poly"),
nadj = NULL,
order = NULL,
select_model = FALSE,
model_params = list(key = list("hn", "hr", "unif"), adjustment = list("cos", "herm",
"poly"), nadj = list(0, 1, 2), order = NULL),
field_of_view = 42,
availability,
n_bootstrap = 100,
n_cores = 1,
...
)
Arguments
- data
A data frame containing distance sampling observations. Must include columns for distance measurements and can include covariates for detection function modeling. See Distance::flatfile for details.
- estimate
Character string specifying the parameter to estimate. Either
"density"
(animals per km^2) or"abundance"
(total number of animals). Default is"density"
.- cutpoints
if the data are binned, this vector gives the cutpoints of the bins. Supplying a distance column in your data and specifying cutpoints is the recommended approach for all standard binned analyses. Ensure that the first element is 0 (or the left truncation distance) and the last is the distance to the end of the furthest bin. (Default
NULL
, no binning.) If you have provideddistbegin
anddistend
columns in your data (note this should only be used when your cutpoints are not constant across all your data, e.g. planes flying at differing altitudes) then do not specify the cutpoints argument as this will cause thedistbegin
anddistend
columns in your data to be overwritten.- truncation
either truncation distance (numeric, e.g. 5) or percentage (as a string, e.g. "15%"). Can be supplied as a
list
with elementsleft
andright
if left truncation is required (e.g.list(left=1,right=20)
orlist(left="1%",right="15%")
or evenlist(left="1",right="15%")
). By default for exact distances the maximum observed distance is used as the right truncation. When the data is binned, the right truncation is the largest bin end point. Default left truncation is set to zero.- formula
formula for the scale parameter. For a CDS analysis leave this as its default
~1
.- key
key function to use;
"hn"
gives half-normal (default),"hr"
gives hazard-rate and"unif"
gives uniform. Note that if uniform key is used, covariates cannot be included in the model.- adjustment
adjustment terms to use;
"cos"
gives cosine (default),"herm"
gives Hermite polynomial and"poly"
gives simple polynomial. A value ofNULL
indicates that no adjustments are to be fitted.- nadj
the number of adjustment terms to fit. In the absence of covariates in the formula, the default value (
NULL
) will select via AIC (using a sequential forward selection algorithm) up tomax.adjustment
adjustments (unlessorder
is specified). When covariates are present in the model formula, the default value ofNULL
results in no adjustment terms being fitted in the model. A non-negative integer value will cause the specified number of adjustments to be fitted. Supplying an integer value will allow the use of adjustment terms in addition to specifying covariates in the model. The order of adjustment terms used will depend on thekey
andadjustment
. Forkey="unif"
, adjustments of order 1, 2, 3, ... are fitted whenadjustment = "cos"
and order 2, 4, 6, ... otherwise. Forkey="hn"
or"hr"
adjustments of order 2, 3, 4, ... are fitted whenadjustment = "cos"
and order 4, 6, 8, ... otherwise. See Buckland et al. (2001, p. 47) for details.- order
order of adjustment terms to fit. The default value (
NULL
) results inds
choosing the orders to use - seenadj
. Otherwise a scalar positive integer value can be used to fit a single adjustment term of the specified order, and a vector of positive integers to fit multiple adjustment terms of the specified orders. For simple and Hermite polynomial adjustments, only even orders are allowed. The number of adjustment terms specified here must matchnadj
(ornadj
can be the defaultNULL
value).- select_model
Logical. If
TRUE
, performs automated model selection using the procedure in Howe et al. (2019). IfFALSE
(default), fits a single model with specified parameters. WhenTRUE
,model_param
defines the candidate model set.- model_params
Named list defining candidate models for selection when
select_model = TRUE
. Elements can include:key
- List of key functions to testadjustment
- List of adjustment typesnadj
- List of adjustment term numbersorder
- List vector of adjustment orders (must matchnadj
)
- field_of_view
Numeric. Camera field of view angle in degrees. Default is 42 deg, ued to calculate the sampling fraction.
- availability
A list containing availability rate corrections (output from
ct_availability()
). Must include elements availability rate (0-1) and/or standard error of availability rate- n_bootstrap
Integer. Number of bootstrap replicates for variance estimation of density/abundance. Default is 100. Larger values provide more precise confidence intervals but increase computation time.
- n_cores
Integer. Number of CPU cores to use for parallel bootstrap computation. Default is 1.
- ...
Arguments passed on to
Distance::ds
scale
the scale by which the distances in the adjustment terms are divided. Defaults to
"width"
, scaling by the truncation distance. If the key is uniform only"width"
will be used. The other option is"scale"
: the scale parameter of the detectiondht_group
should density abundance estimates consider all groups to be size 1 (abundance of groups)
dht_group=TRUE
or should the abundance of individuals (group size is taken into account),dht_group=FALSE
. Default isFALSE
(abundance of individuals is calculated).monotonicity
should the detection function be constrained for monotonicity weakly (
"weak"
), strictly ("strict"
) or not at all ("none"
orFALSE
). See Monotonicity, below. (Default"strict"
). By default it is on for models without covariates in the detection function, off when covariates are present.method
optimization method to use (any method usable by
optim
oroptimx
). Defaults to"nlminb"
.mono_method
optimization method to use when monotonicity is enforced. Can be either
slsqp
orsolnp
. Defaults toslsqp
.initial_values
a
list
of named starting values, seemrds_opt
. Only allowed when AIC term selection is not used.max_adjustments
maximum number of adjustments to try (default 5) only used when
order=NULL
.er_method
encounter rate variance calculation: default = 2 gives the method of Innes et al, using expected counts in the encounter rate. Setting to 1 gives observed counts (which matches Distance for Windows) and 0 uses binomial variance (only useful in the rare situation where study area = surveyed area). See
dht.se
for more details.dht_se
should uncertainty be calculated when using
dht
? Safe to leave asTRUE
, used inbootdht
.optimizer
By default this is set to 'both'. In this case the R optimizer will be used and if present the MCDS optimizer will also be used. The result with the best likelihood value will be selected. To run only a specified optimizer set this value to either 'R' or 'MCDS'. See
mcds_dot_exe
for setup instructions.winebin
If you are trying to use our MCDS.exe optimizer on a non-windows system then you may need to specify the winebin. Please see
mcds_dot_exe
for more details.
Value
A named list containing: A list containing:
QAIC
: (Only ifselect_model = TRUE
) QAIC comparison table.Chi2
: (Only ifselect_model = TRUE
) Chi-squared goodness-of-fit comparison.best_model
: The best fitted detection function model selected.rho
: Estimated effective detection radius (in meters).density
orabundance
: A tibble with density or abundance estimates containing:median
,mean
,se
: standard error,lcl
: lower confidence limit,ucl
: upper confidence limit
Truncation
The right truncation point is by default set to be largest observed distance or bin end point. This is a default will not be appropriate for all data and can often be the cause of model convergence failures. It is recommended that one plots a histogram of the observed distances prior to model fitting so as to get a feel for an appropriate truncation distance. (Similar arguments go for left truncation, if appropriate). Buckland et al (2001) provide guidelines on truncation.
When specified as a percentage, the largest right
and smallest left
percent distances are discarded. Percentages cannot be supplied when using
binned data.
For left truncation, there are two options: (1) fit a detection function to
the truncated data as is (this is what happens when you set left
). This
does not assume that g(x)=1 at the truncation point. (2) manually remove
data with distances less than the left truncation distance – effectively
move the centre line out to be the truncation distance (this needs to be
done before calling ds
). This then assumes that detection is certain at
the left truncation distance. The former strategy has a weaker assumption,
but will give higher variance as the detection function close to the line
has no data to tell it where to fit – it will be relying on the data from
after the left truncation point and the assumed shape of the detection
function. The latter is most appropriate in the case of aerial surveys,
where some area under the plane is not visible to the observers, but their
probability of detection is certain at the smallest distance.
Monotonicity
When adjustment terms are used, it is possible for the detection function to not always decrease with increasing distance. This is unrealistic and can lead to bias. To avoid this, the detection function can be constrained for monotonicity (and is by default for detection functions without covariates).
Monotonicity constraints are supported in a similar way to that described
in Buckland et al (2001). 20 equally spaced points over the range of the
detection function (left to right truncation) are evaluated at each round
of the optimisation and the function is constrained to be either always
less than it's value at zero ("weak"
) or such that each value is
less than or equal to the previous point (monotonically decreasing;
"strict"
). See also check.mono
.
Even with no monotonicity constraints, checks are still made that the
detection function is monotonic, see check.mono
.
Data format
One can supply data
only to simply fit a detection function. However, if
abundance/density estimates are necessary further information is required.
Either the region_table
, sample_table
and obs_table
data.frame
s can
be supplied or all data can be supplied as a "flat file" in the data
argument. In this format each row in data has additional information that
would ordinarily be in the other tables. This usually means that there are
additional columns named: Sample.Label
, Region.Label
, Effort
and
Area
for each observation. See flatfile
for an example.
Clusters/groups
Note that if the data contains a column named size
, cluster size will be
estimated and density/abundance will be based on a clustered analysis of
the data. Setting this column to be NULL
will perform a non-clustered
analysis (for example if "size
" means something else in your dataset).
References
Buckland, S.T., Anderson, D.R., Burnham, K.P., Laake, J.L., Borchers, D.L., and Thomas, L. (2001). Distance Sampling. Oxford University Press. Oxford, UK.
Howe, E. J., Buckland, S. T., Després-Einspenner, M., & Kühl, H. S. (2017). Distance sampling with camera traps. Methods in Ecology and Evolution, 8(11), 1558-1565. doi:10.1111/2041-210X.12790
Howe, E. J., Buckland, S. T., Després-Einspenner, M., & Kühl, H. S. (2019). Model selection with overdispersed distance sampling data. Methods in Ecology and Evolution, 10(1), 38-47. doi:10.1111/2041-210X.13082
Rowcliffe, J. M., Kays, R., Kranstauber, B., Carbone, C., & Jansen, P. A. (2014). Quantifying levels of animal activity using camera trap data. Methods in Ecology and Evolution, 5(11), 1170-1179. doi:10.1111/2041-210X.12278
Examples
if (FALSE) { # \dontrun{
data("duikers")
# Calculates animal availability adjustment factor
trigger_events <- duikers$VideoStartTimesFullDays
avail <- ct_availability(times = trigger_events$time,
format = "%H:%M", n_bootstrap = 100)
# Estimate density, building multiple models
flat_data <- duikers$DaytimeDistances %>%
dplyr::slice_sample(prop = .2) # sample 20% of rows
duiker_density <- ct_fit_ds(data = flat_data,
estimate = "density",
select_model = TRUE,
model_params = list(key = list("hn", "hr"),
adjustment = list("cos"),
nadj = list(2, 3),
order = NULL),
availability = avail,
truncation = list(left = 2, right = 15),
field_of_view = 42,
n_bootstrap = 2,
cutpoints = c(seq(2, 8, 1), 10, 12, 15)
)
# View density
duiker_density$density
} # }