Title: | Estimation of Caribou Abundance Based on Radio Telemetry Data |
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Description: | Estimation of population size of migratory caribou herds based on large scale aggregations monitored by radio telemetry. It implements the methodology found in the article by Rivest et al. (1998) about caribou abundance estimation. It also includes a function based on the Lincoln-Petersen Index as applied to radio telemetry data by White and Garrott (1990). |
Authors: | Louis-Paul Rivest [aut, cre], Helene Crepeau [aut], Serge Couturier [ctb], Sophie Baillargeon [aut] |
Maintainer: | Louis-Paul Rivest <[email protected]> |
License: | GPL-2 |
Version: | 1.1-1 |
Built: | 2024-10-31 22:13:02 UTC |
Source: | CRAN |
Estimation of population size of migratory caribou herds based on large scale aggregations monitored by radio telemetry. It implements the methodology found in the article by Rivest et al. (1998) about caribou abundance estimation. It also includes a function based on the Lincoln-Petersen Index as applied to radio telemetry data by White and Garrott (1990).
Package: | caribou |
Type: | Package |
Version: | 1.1-1 |
Date: | 2022-04-13 |
License: | GPL-2 |
CONTEXT:
Migratory caribou forms aggregations at different seasons in their yearly life cycle,
namely in the spring and fall migration, and also in summer following insect harassment.
Postcalving aggregations that happened in July under warm and calm conditions
are the most impressive and they are well known for long time by caribou biologists
and by indigenous people. The Inuit that lived also in the tundra with caribou described
this spectacular animal behavior as the moving mountains.
Rivest et al. (1998) proposed a new method for estimating caribou herd size based on
photo-census of large scale aggregations. This method can also be used in other time
of the year for caribou or for other wildlife species that live in open habitat like tundra.
Here we provided some dataset examples for postcalving census done in Quebec and
elsewhere in North America.
If you are using this tool to estimate wildlife abundance, please let us know
and quote this paper:
Rivest, L.-P., Couturier, S. and Crepeau, H. (1998). Statistical Methods for estimating caribou abundance
using postcalving aggregations detected by radio telemetry. Biometrics, 54(3), 865-876.
Louis-Paul Rivest [email protected] and
Helene Crepeau [email protected] and
Serge Couturier [email protected] and
Sophie Baillargeon [email protected]
Rivest, L.-P., Couturier, S. and Crepeau, H. (1998). Statistical Methods for estimating caribou abundance using postcalving aggregations detected by radio telemetry. Biometrics, 54(3), 865-876.
White, G.C. and Garrott, R.A. (1990). Analysis of wildlife radio-tracking data. San Diego: Academic Press.
The function abundance
applies the methodology found in Rivest et al. (1998) for estimating
caribou abundance using postcalving aggregations detected by radio telemetry.
abundance(mat, n, model = c("H", "I", "T"), B, maxT.hat) ## S3 method for class 'abundance' print(x,...)
abundance(mat, n, model = c("H", "I", "T"), B, maxT.hat) ## S3 method for class 'abundance' print(x,...)
mat |
A matrix containing in the first column the number of radio-collared animals in the detected (photographed) groups and in the second column the corresponding size of the detected groups. |
n |
A numeric: the total number of active collars during the census. |
model |
A character string indicating the model to determine the probability that a group with
collared animals is detected |
B |
A numeric: a bound for the threshold model. |
maxT.hat |
A numeric: an upper bound used in the numerical computation of |
x |
An object, produced by the |
... |
Further arguments to be passed to methods (see |
DETECTION MODELS
- homogeneity model (model="H"
):
- independence model (model="I"
):
- threshold model (model="T"
):
where is the probability that a group with collared animals is detected,
is the number of radio-collared in the detected (photographed) groups and
is a parameter related to the probability of detection.
For the threshold model,
B
is a bound given as a function's argument.
mp |
The number of detected groups having radio-collared animals. |
xt |
The total number of radio-collared animals found in the detected groups. |
gnt |
The total number of animals counted in the detected groups. |
rr |
The estimated parameter related to the probability of detection. |
se_rr |
The estimated standard error of |
mat_pi |
A matrix containing a sorted copy of the input matrix |
T.hat |
The estimator for the total number of animals in a herd. |
se_T.hat |
The estimated standard error of |
loglikelihood |
The maximum value of the loglikelihood function for the detected model. |
randomness_test |
A vector with the statistic and the p-value of a score test for the randomness assumption available only for the homogeneity, independence and threshold model with B=2 or 3. |
call |
The function call (object of class "call"). |
Louis-Paul Rivest [email protected] and
Helene Crepeau [email protected] and
Serge Couturier [email protected] and
Sophie Baillargeon [email protected]
Rivest, L.-P., Couturier, S. and Crepeau, H. (1998). Statistical Methods for estimating caribou abundance using postcalving aggregations detected by radio telemetry. Biometrics, 54(3), 865-876.
data(GRH93) abundance(GRH93, n=92) # default model="H" abundance(GRH93, n=92, model="H") abundance(GRH93, n=92, model="I") abundance(GRH93, n=92, model="T", B=2) abundance(GRH93, n=92, model="T", B=4) abundance(GRH93, n=92, model="T", B=6)
data(GRH93) abundance(GRH93, n=92) # default model="H" abundance(GRH93, n=92, model="H") abundance(GRH93, n=92, model="I") abundance(GRH93, n=92, model="T", B=2) abundance(GRH93, n=92, model="T", B=4) abundance(GRH93, n=92, model="T", B=6)
Population size of the Bluenose-East caribou herd (Northwest Territories, Canada) from a postcalving survey in June-July 2000.
data(BEH00)
data(BEH00)
16 by 2 numeric matrix, with the following columns:
xi
number of radio-collared animals in the detected (photographed) groups
gni
size of the detected groups
During this survey, 33 collars were active (Patterson et al. also made calculation considering that
30 collars were active because 3 caribou were never located after collaring).
23 collars (70%) were photographed among the 16 detected groups.
This data set excludes the six groups without radio-collared animal from Table 1 of Patterson et al.
(2004) since they cannot be included in the estimates of the total population size.
For the last three groups, the size gni
has been modified according to what Patterson et al.
(2004) did (38% of what appears in Table 1).
Patterson, B. R., Olsen, B. T. and Joly, D. O. (2004). Population estimate for the Bluenose-East caribou herd using post-calving photography. Arctic, 57, 47-58.
petersen(BEH00, M=33) abundance(BEH00, n=33, model="H")
petersen(BEH00, M=33) abundance(BEH00, n=33, model="H")
Population size of the George River (Riviere George) herd (Quebec) from a postcalving survey in July 2001.
data(GRH01)
data(GRH01)
27 by 2 numeric matrix, with the following columns:
xi
number of radio-collared animals in the detected (photographed) groups
gni
size of the detected groups
During this survey, 109 collars were active.
56 collars (57%) were photographed among the 27 detected groups.
Couturier, S., Jean, D., Otto, R. and Rivard, S. (2004). Demography of the migratory tundra caribou (Rangifer tarandus) of the Nord-du-Quebec region and Labrador. Min. Ressources naturelles, Faune et Parcs, Quebec. 68 p. ISBN: 2-550-43725-X
petersen(GRH01, M=109) abundance(GRH01, n=109, model="H") abundance(GRH01, n=109, model="I") abundance(GRH01, n=109, model="T", B=2) abundance(GRH01, n=109, model="T", B=4) abundance(GRH01, n=109, model="T", B=6)
petersen(GRH01, M=109) abundance(GRH01, n=109, model="H") abundance(GRH01, n=109, model="I") abundance(GRH01, n=109, model="T", B=2) abundance(GRH01, n=109, model="T", B=4) abundance(GRH01, n=109, model="T", B=6)
Population size of the George River (Riviere George) herd (Quebec) from a postcalving survey in July 2010.
data(GRH10)
data(GRH10)
13 by 2 numeric matrix, with the following columns:
xi
number of radio-collared animals in the detected (photographed) groups
gni
size of the detected groups
During this survey, 71 collars were active.
43 collars (61%) were photographed among the 13 detected groups.
Couturier, S., unpubl. data
petersen(GRH10, M=71) petersen(GRH10, M=71, S=1000) abundance(GRH10, n=71, model="H") abundance(GRH10, n=71, model="I") abundance(GRH10, n=71, model="T", B=2) abundance(GRH10, n=71, model="T", B=4) abundance(GRH10, n=71, model="T", B=6)
petersen(GRH10, M=71) petersen(GRH10, M=71, S=1000) abundance(GRH10, n=71, model="H") abundance(GRH10, n=71, model="I") abundance(GRH10, n=71, model="T", B=2) abundance(GRH10, n=71, model="T", B=4) abundance(GRH10, n=71, model="T", B=6)
Population size of the George River (Riviere George) herd (Quebec and Labrador) from a postcalving survey in July 1993.
data(GRH93)
data(GRH93)
28 by 2 numeric matrix, with the following columns:
xi
number of radio-collared animals in the detected (photographed) groups
gni
size of the detected groups
During this survey, 92 collars were active.
73 collars (79%) were photographed among the 28 detected groups.
Rivest, L.-P., Couturier, S. and Crepeau, H. (1998). Statistical Methods for estimating caribou abundance using postcalving aggregations detected by radio telemetry. Biometrics, 54(3), 865-876.
petersen(GRH93, M=92) petersen(GRH93, M=92, S=4000) abundance(GRH93, n=92, model="H") abundance(GRH93, n=92, model="I") abundance(GRH93, n=92, model="T", B=2) abundance(GRH93, n=92, model="T", B=4) abundance(GRH93, n=92, model="T", B=6)
petersen(GRH93, M=92) petersen(GRH93, M=92, S=4000) abundance(GRH93, n=92, model="H") abundance(GRH93, n=92, model="I") abundance(GRH93, n=92, model="T", B=2) abundance(GRH93, n=92, model="T", B=4) abundance(GRH93, n=92, model="T", B=6)
Population size of the Leaf River (Riviere aux Feuilles) herd (Quebec) from a postcalving survey in July 2001.
data(LRH01)
data(LRH01)
17 by 2 numeric matrix, with the following columns:
xi
number of radio-collared animals in the detected (photographed) groups
gni
size of the detected groups
During this survey, 120 collars were active.
23 collars (19%) were photographed among the 17 detected groups.
The small sample size of this census was caused by technical and weather related problems in July 2001. This provided an opportunity to see the behaviour of the different models under low sampling regime.
Couturier, S., Jean, D., Otto, R. and Rivard, S. (2004). Demography of the migratory tundra caribou (Rangifer tarandus) of the Nord-du-Quebec region and Labrador. Min. Ressources naturelles, Faune et Parcs, Quebec. 68 p. ISBN: 2-550-43725-X
petersen(LRH01, M=120) abundance(LRH01, n=120, model="H") abundance(LRH01, n=120, model="I") abundance(LRH01, n=120, model="T", B=2) # The threshold model with B >= 3 is equivalent # to the homogeneity model for this data set # because max(LRH01$xi)=2
petersen(LRH01, M=120) abundance(LRH01, n=120, model="H") abundance(LRH01, n=120, model="I") abundance(LRH01, n=120, model="T", B=2) # The threshold model with B >= 3 is equivalent # to the homogeneity model for this data set # because max(LRH01$xi)=2
The function petersen
estimates the total population size based on the Lincoln-Petersen Index
as applied to radio telemetry data by White and Garrott (1990). It uses the Lincoln-Petersen estimator
with Chapman's (1951) bias correction and the bias corrected standard error estimator of
Seber (1970) and Wittes (1972).
petersen(mat, M, S = 0) ## S3 method for class 'petersen' print(x,...)
petersen(mat, M, S = 0) ## S3 method for class 'petersen' print(x,...)
mat |
A matrix containing in the first column the number of radio-collared animals in the detected (photographed) groups and in the second column the corresponding size of the detected groups. |
M |
A numeric: the total number of active collars during the census
(equivalent to the argument |
S |
A numeric: the minimum size that define well aggregated groups. Only observations
from well aggregated groups (containing at least |
x |
An object, produced by the |
... |
Further arguments to be passed to methods (see |
G |
The number of well aggregated groups. |
R |
The total number of radio-collared animal observed in the well aggregated groups. |
C |
The total number of animals observed in the well aggregated groups containing at least one radio-collared animal during the survey. |
T.hat |
The modified lincoln-Petersen estimator for the total number of animals in a herd. |
se_T.hat |
The estimated standard error of |
mat_aggre |
A matrix containing a subset of the input matrix |
call |
The function call (object of class "call"). |
Louis-Paul Rivest [email protected] and
Helene Crepeau [email protected] and
Serge Couturier [email protected] and
Sophie Baillargeon [email protected]
Chapman, D. G. (1951). Some properties of the hypergeometric distribution with applications to zoological sample censuses. University of California Publications in Statistics, 1(7), 131-160.
Seber, G.A.F. (1970). The effects of trap response on tag recapture estimates. Biometrics, 26, 13-22.
White, G.C. and Garrott, R.A. (1990). Analysis of wildlife radio-tracking data. San Diego: Academic Press.
Wittes, J.T. (1972). On the bias and estimated variance of Chapman's two-sample capture-recapture population estimate. Biometrics, 28, 592-597.
data(GRH93) petersen(GRH93, M=92) # default S=0 petersen(GRH93, M=92, S=4000)
data(GRH93) petersen(GRH93, M=92) # default S=0 petersen(GRH93, M=92, S=4000)
Population size of the Western Arctic Herd (Alaska) from a postcalving survey in 2011.
data(WAH11)
data(WAH11)
10 by 2 numeric matrix, with the following columns:
xi
number of radio-collared animals in the detected (photographed) groups
gni
size of the detected groups
During this survey, 97 collars were active.
96 collars (99%) were photographed among the 10 detected groups.
This data set provide the opportunity to test the models under very high sampling regime.
Dau, J., unpubl. data
petersen(WAH11, M=97) abundance(WAH11, n=97, model="H") abundance(WAH11, n=97, model="I") abundance(WAH11, n=97, model="T", B=2)
petersen(WAH11, M=97) abundance(WAH11, n=97, model="H") abundance(WAH11, n=97, model="I") abundance(WAH11, n=97, model="T", B=2)