Conservation Science and Practice,
Journal Year:
2020,
Volume and Issue:
2(10)
Published: Sept. 5, 2020
Abstract
Outdoor
recreation
is
one
of
the
fastest
growing
economic
sectors
in
world
and
provides
many
benefits
to
people.
Assessing
possible
negative
impacts
nevertheless
important
for
sustainable
management.
Here,
we
used
camera
traps
assess
relative
effects
various
recreational
activities—as
compared
each
other
environmental
conditions—on
a
terrestrial
wildlife
assemblage
British
Columbia,
Canada.
Across
13
species,
only
two
associations
between
activities
detections
were
observed
at
weekly
scales:
mountain
biking
on
moose
grizzly
bears.
However,
finer‐scale
analysis
showed
that
all
species
avoided
humans
trails,
with
avoidance
strongest
motorized
vehicles.
Our
results
imply
factors
generally
shaped
broad‐scale
patterns
use,
but
highlight
also
have
detectable
impacts.
These
can
be
monitored
using
same
camera‐trapping
techniques
are
commonly
monitor
assemblages.
Journal of Applied Ecology,
Journal Year:
2015,
Volume and Issue:
52(3), P. 675 - 685
Published: March 24, 2015
Summary
Reliable
assessment
of
animal
populations
is
a
long‐standing
challenge
in
wildlife
ecology.
Technological
advances
have
led
to
widespread
adoption
camera
traps
(
CT
s)
survey
distribution,
abundance
and
behaviour.
As
for
any
method,
trapping
must
contend
with
sources
sampling
error
such
as
imperfect
detection.
Early
applications
focused
on
density
estimation
naturally
marked
species,
but
there
growing
interest
broad‐scale
surveys
unmarked
communities.
Nevertheless,
inferences
based
detection
indices
are
controversial,
the
suitability
alternatives
occupancy
debatable.
We
reviewed
266
studies
published
between
2008
2013.
recorded
study
objectives
methodologies,
evaluating
consistency
protocols
designs,
extent
which
considered
error,
linkages
analytical
assumptions
species
Nearly
two‐thirds
surveyed
more
than
one
majority
used
response
variables
that
ignored
(e.g.
presence–absence,
relative
abundance).
Many
opportunistic
did
not
explicitly
report
details
design
deployment
could
affect
conclusions.
Most
estimating
capture–recapture
methods
spatially
explicit
becoming
prominent.
Few
estimated
focusing
instead
modelling
or
measures
abundance.
While
detectability,
most
define
key
components
framework
site)
discuss
potential
violations
model
site
closure).
Studies
using
relied
equal
expected
relationships
measured
responses
underlying
ecological
processes
movement).
Synthesis
.
The
rapid
represents
an
exciting
transition
methodology.
remain
optimistic
about
technology's
promise,
call
consideration
abundance,
movement
by
cameras,
including
thorough
reporting
methodological
assumptions.
Such
transparency
will
facilitate
efforts
evaluate
improve
reliability
trap
surveys,
ultimately
leading
stronger
helping
meet
modern
needs
effective
inquiry
biodiversity
monitoring.
Global Ecology and Biogeography,
Journal Year:
2014,
Volume and Issue:
23(12), P. 1472 - 1484
Published: Aug. 8, 2014
Abstract
Aim
During
the
past
decade
ecologists
have
attempted
to
estimate
parameters
of
species
distribution
models
by
combining
locations
presence
observed
in
opportunistic
surveys
with
spatially
referenced
covariates
occurrence.
Several
statistical
been
proposed
for
analysis
presence‐only
data,
but
these
largely
ignored
effects
imperfect
detection
and
survey
bias.
In
this
paper
I
describe
a
model‐based
approach
data
that
accounts
errors
individuals
biased
selection
locations.
Innovation
develop
hierarchical,
model
allows
be
analysed
conjunction
acquired
independently
planned
surveys.
One
component
specifies
spatial
within
bounded,
geographic
region
as
realization
point
process.
A
second
two
kinds
observations,
encountered
during
Main
conclusions
Using
mathematical
proof
simulation‐based
comparisons,
demonstrate
biases
induced
or
can
reduced
eliminated
using
hierarchical
analyse
counts
show
relatively
small
number
high‐quality
(from
surveys)
used
leverage
information
which
usually
broad
coverage
may
not
informative
both
occurrence
detectability
individuals.
Because
variety
sampling
protocols
surveys,
is
widely
applicable.
addition,
since
point‐process
formulated
at
level
an
individual,
it
extended
account
biological
interactions
between
temporal
changes
their
distributions.
Methods in Ecology and Evolution,
Journal Year:
2013,
Volume and Issue:
5(12), P. 1269 - 1279
Published: July 24, 2013
Summary
The
past
decade
has
seen
an
explosion
in
the
development
and
application
of
models
aimed
at
estimating
species
occurrence
occupancy
dynamics
while
accounting
for
possible
non‐detection
or
misidentification.
We
discuss
some
recent
estimation
methods
biological
systems
that
motivated
their
development.
Collectively,
these
offer
tremendous
flexibility,
but
simultaneously
place
added
demands
on
investigator.
Unlike
many
mark–recapture
scenarios,
investigators
utilizing
have
ability,
responsibility,
to
define
sample
units
(i.e.
sites),
replicate
sampling
occasions,
time
period
over
which
is
assumed
be
static
even
criteria
constitute
‘detection’
a
target
species.
Subsequent
inference
interpretation
model
parameters
depend
definitions
ability
meet
assumptions.
demonstrate
relevance
by
highlighting
applications
from
single
system
(an
amphibian–pathogen
system)
situations
where
use
been
criticized.
Finally,
we
suggest
future
research
Ecological Monographs,
Journal Year:
2018,
Volume and Issue:
88(4), P. 526 - 542
Published: May 15, 2018
Abstract
Checking
that
models
adequately
represent
data
is
an
essential
component
of
applied
statistical
inference.
Ecologists
increasingly
use
hierarchical
Bayesian
in
their
research.
The
appeal
this
modeling
paradigm
undeniable,
as
researchers
can
build
and
fit
embody
complex
ecological
processes
while
simultaneously
accounting
for
observation
error.
However,
ecologists
tend
to
be
less
focused
on
checking
model
assumptions
assessing
potential
lack
when
applying
methods
than
more
traditional
modes
inference
such
maximum
likelihood.
There
are
also
multiple
ways
the
models,
each
which
has
strengths
weaknesses.
For
instance,
P
values
relatively
easy
compute,
but
well
known
conservative,
producing
biased
toward
0.5.
Alternatively,
lesser
approaches
checking,
prior
predictive
checks,
cross‐validation
probability
integral
transforms,
pivot
discrepancy
measures
may
produce
accurate
characterizations
goodness‐of‐fit
not
ecologists.
In
addition,
a
suite
visual
targeted
diagnostics
used
examine
violations
different
at
levels
hierarchy,
check
residual
temporal
or
spatial
autocorrelation.
review,
we
synthesize
existing
literature
guide
through
many
available
options
checking.
We
illustrate
procedures
with
several
case
studies
including
(1)
analysis
simulated
spatiotemporal
count
data,
(2)
N‐mixture
estimating
abundance
sea
otters
from
aircraft,
(3)
hidden
Markov
describe
attendance
patterns
California
lion
mothers
rookery.
find
commonly
based
posterior
detect
extreme
inadequacy,
often
do
subtle
cases
fit.
Tests
(including
“sampled
value”)
appear
better
suited
have
overall
performance.
conclude
necessary
ensure
scientific
founded.
As
discovery,
it
should
accompany
most
analyses
presented
literature.
Methods in Ecology and Evolution,
Journal Year:
2020,
Volume and Issue:
11(6), P. 700 - 713
Published: Feb. 4, 2020
Abstract
Camera
traps
deployed
in
grids
or
stratified
random
designs
are
a
well‐established
survey
tool
for
wildlife
but
there
has
been
little
evaluation
of
study
design
parameters.
We
used
an
empirical
subsampling
approach
involving
2,225
camera
deployments
run
at
41
areas
around
the
world
to
evaluate
three
aspects
trap
(number
sites,
duration
and
season
sampling)
their
influence
on
estimation
ecological
metrics
(species
richness,
occupancy
detection
rate)
mammals.
found
that
25–35
sites
were
needed
precise
estimates
species
depending
scale
study.
The
precision
species‐level
(ψ)
was
highly
sensitive
level,
with
<20
common
(ψ
>
0.75)
species,
more
than
150
likely
rare
<
0.25)
species.
Species
rates
difficult
estimate
precisely
grid
level
due
spatial
heterogeneity,
presumably
driven
by
unaccounted
habitat
variability
factors
within
area.
Running
site
2
weeks
most
efficient
detecting
new
3–4
local
rate,
no
gains
observed
after
1
month.
Metrics
all
mammal
communities
seasonality,
37%–50%
we
examined
fluctuating
significantly
over
year.
This
effect
pronounced
temperate
where
seasonally
varied
relative
abundance
average
factor
4–5,
some
completely
absent
one
hibernation
migration.
recommend
following
guidelines
efficiently
obtain
arrays:
each
3–5
across
40–60
per
array.
comparisons
be
model
based
include
covariates
help
account
small‐scale
variation.
Furthermore,
times
must
which
could
have
strong
impacts
both
tropical
sites.
African Journal of Ecology,
Journal Year:
2018,
Volume and Issue:
56(4), P. 740 - 749
Published: Nov. 29, 2018
Abstract
Camera
traps
are
increasingly
used
to
study
wildlife
ecology
and
inform
conservation,
but
valid
inference
depends
on
appropriate
data
analysis.
This
article
introduces
the
most
common
analytical
approaches
for
camera‐trap
data.
generally
as
point‐based
sampling
devices,
many
methods
require
spatial
independence
of
stations
temporal
subsequent
records.
Photographic
rates
species
should
be
interpreted
with
care,
because
they
confound
abundance/use
detectability.
Occupancy
models
estimate
occurrence
while
accounting
imperfect
detection
can
reveal
species–habitat
associations.
Capture–recapture
abundance
probability
from
individual
detection/nondetection
applicable
individually
recognizable
species.
Spatial
capture–recapture
extends
this
framework
by
animal
movement
location
relative
trap
array.
is
particularly
useful
often
wide‐ranging
typically
studied
camera
presents
possibilities
modelling
population
processes.
Several
have
been
developed
that
cannot
identified;
all
heavily
rely
model
assumptions.
Finally,
time
stamps
records
describe
activity
pattern
interactions
between
Considering
usefulness
trapping,
we
expect
ongoing
development
Journal of Applied Ecology,
Journal Year:
2015,
Volume and Issue:
52(2), P. 413 - 421
Published: Jan. 28, 2015
Summary
Over
the
last
two
decades,
a
large
number
of
camera
trap
surveys
have
been
carried
out
around
world
and
traps
proposed
as
an
ideal
tool
for
inventorying
monitoring
medium
to
large‐sized
terrestrial
vertebrates.
However,
few
studies
analysed
data
at
community
level.
We
developed
multi‐session
multi‐species
occupancy
model
that
allows
us
obtain
estimates
species
richness
combining
from
multiple
(sessions).
By
estimating
presence
session‐level
modelling
detection
probability
each
sessions
nested
random
effects,
we
could
improve
parameter
session,
especially
with
sparse
data.
variants
our
model:
one
was
binary
latent
states
while
other
used
Royle–Nichols
formulation
relationship
between
abundance.
applied
both
models
eight
south‐eastern
Peru
including
six
study
sites,
263
stations
17
423
days.
Sites
covered
protected
areas,
logging
concession
Brazil
nut
concessions.
included
habitat
(
terra
firme
vs.
floodplain)
covariate
trail
off‐trail
detection.
Among‐camera
heterogeneity
serious
problem
variant
had
much
better
fit
than
binary‐state
variant.
Both
resulted
in
similar
showing
most
sites
contained
intact
mammal
communities.
Detection
probabilities
values
were
more
variable
across
within
species.
Three
showed
preference
four
or
avoidance
trails.
Synthesis
applications
.
Our
provides
improved
set.
is
ideally
suited
integrating
numbers
sets
investigate
regional
and/or
temporal
patterns
distribution
composition
communities
relation
natural
anthropogenic
factors
monitor
over
time.
Global Change Biology,
Journal Year:
2021,
Volume and Issue:
27(16), P. 3718 - 3731
Published: April 22, 2021
Abstract
Human
activity
and
land
use
change
impact
every
landscape
on
Earth,
driving
declines
in
many
animal
species
while
benefiting
others.
Species
ecological
life
history
traits
may
predict
success
human‐dominated
landscapes
such
that
only
with
“winning”
combinations
of
will
persist
disturbed
environments.
However,
this
link
between
successful
coexistence
humans
remains
obscured
by
the
complexity
anthropogenic
disturbances
variability
among
study
systems.
We
compiled
detection
data
for
24
mammal
from
61
populations
across
North
America
to
quantify
effects
(1)
direct
presence
people
(2)
human
footprint
(landscape
modification)
occurrence
levels.
Thirty‐three
percent
exhibited
a
net
negative
response
(i.e.,
reduced
or
activity)
increasing
and/or
populations,
whereas
58%
were
positively
associated
disturbance.
apparent
benefits
tended
decrease
disappear
at
higher
disturbance
levels,
indicative
thresholds
species’
capacity
tolerate
exploit
landscapes.
strong
predictors
their
responses
footprint,
favoring
smaller,
less
carnivorous,
faster‐reproducing
species.
The
positive
distributed
more
randomly
respect
trait
values,
winners
losers
range
body
sizes
dietary
guilds.
Differential
some
highlight
importance
considering
these
two
forms
separately
when
estimating
impacts
wildlife.
Our
approach
provides
insights
into
complex
mechanisms
through
which
activities
shape
communities
globally,
revealing
drivers
loss
larger
predators
human‐modified