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sample survey advantages
cost effective and efficient
can gain insights into the broader population trends and patterns
non probability sampling
convenience based
judgement based
targeted sampling
simple random sampling
each unit has an equal chance of being selected
systematic sampling
samples taken at regular intervals after a random start
stratified sampling
the population is divided into strata, and random samples are taken from each
cluster sampling
the population is divided into clusters, and random samples of clusters are taken
simple random sampling process
identify all possible sampling units and randomly select a pre-determined subset #
units size can vary
most appropriate when habitat is homogenous
simple and easy to implement
provides unbiased parameters
could produce bias in situations where animals or habitats features of interest are heterogenous
stratified random sampling process
population of sampling units is divided into strata and samples are randomly taken from each strata
most appropriate for when the habitat and/or organisms of interest are occurring in clear groups or environmentally derived pattern
improves statistical precision by accounting for known variability and ensures representation from all strata
does require a prior understanding of strata
systematic sampling process
samples taken at regular intervals after a random starting point
common in habitat studies
easy to implement and ensures even coverage
can introduce bias if measured variables can a cyclic or other pattern to is distribution
cluster sampling process
population is divided into clusters, and random samples of clusters are taken
used when animals are naturally grouped
cluster size can affect precision
reduces effort and cost when population is large and easier to implement when it is widely spread
increases variability between clusters, reducing precision
fixed radius plot
cruising timber method
record DBH, species, and other variables of all trees within a fixed area
allows the direct calculation of
stem density
basal area
typically extrapolated to represent per-acre or per-hectare estimates
time and labor intensive
variable radius plot
cruising timber method
size of your vegetation plot varies based on the tree size
larger diameter plots for large trees, smaller diameter plots for small trees
prism or angle gause is used to determine if a tree is inside or outside plot boundaries
plot based disadvantages
labor intensive and time-consuming
limited spatial coverage
potential for bias
habitat disturbance
inflexibility
plotless sampling
estimate population parameters based on distance measurements
used to assess the density of natural resources without the need for traditional plots
line intercept sampling
used to estimate the coverage and other parameters of 2-d objects within a study area
line transect assumptions
objects on the line are detected 100%
animals are counted only once
observers do not influence animal movements
objects are fixed at point of initial observation
distances are measured accurately
transect lines are located probabilistically
point count survey
standard method used to estimate the abundance and diversity of a bird species within a specific area
observers stand at predetermined points and count all birds seen or heard within a fixed time period and distance
point and count advantages
relatively simple to conduct
provide quantitative data on bird populations
can be repeated over time to monitor changes
non-invasive
camera trapping
non-invasive technique used to study and monitor wildlife populations
involves the placement of automated camera systems in the field to capture images or videos of animals as they pass by
camera trapping advantages
cost effective, non-invasive
allows for long-term monitoring of wildlife populations without disturbing the animals
provides visual record of species and can capture rare or elusive species
camera trapping limitations
camera placement
battery life
image quality
may not be suitable for all species/habitats
data analysis can be time-consuming
capture-recapture studies
involve sampling the population of interest two or more times
each captured animal uniquely marked to estimate abundance and other population parameters while accounting for imperfect detection
time to event models
use data from radio-tagged individuals to estimate abundance, survival, recruitment, and account for detectability
making assumptions about the random sampling and independence of survival times
occupancy modeling
focus on estimating the proportion of suitable habitat occupied by the species of interest
requiring assumptions about site closure and independent detections
provides a less labor-intensive alternative to abundance estimation
double sampling
easy to measure or inexpensive indicators are measured across a large subset of experimental units then more rigorous or expensive indicators are measured on a smaller subset
usually look for a strong correlation between the two, allowing us to extrapolate and increase confidence and inferential scop
can be adapted to plot, point, or line-based surveys