Data and code from Cappello et al. 2024. Ecosphere.
Data citation:
Cappello, C. D., K. V. Jacobson, J. T. Driscoll, and K. M. McCarty.
2024. Evaluating the effects of nest management on a recovering raptor
using integrated population modeling (v1.0) [Data set]. Zenodo. https://doi.org/10.5281/zenodo.11051071.
Contact:
Caroline Cappello
Email: caroline.d.cappello@gmail.com
ORCID: https://orcid.org/0000-0002-2687-4019
Manuscript abstract:
Evaluating population responses to management is a crucial component of
successful conservation programs. Models predicting population growth
under different management scenarios can provide key insights into the
efficacy of specific management actions both in reversing population
decline and in maintaining recovered populations. Bald eagle
(Haliaeetus leucocephalus) conservation in the United States
has seen many successes over the last 50 years, yet the extent to which
the bald eagle population has recovered in Arizona, an important
population within the Southwest region, remains an area of debate.
Estimates of the species’ population trend and an evaluation of ongoing
nest-level management practices are needed to inform management
decisions. We developed a Bayesian integrated population model (IPM) and
population viability analysis (PVA) using a 36-year dataset to assess
Arizona bald eagle population dynamics and their underlying demographic
rates under current and possible future management practices. We
estimated that the population grew from 87 females in 1993 to 211
females in 2022, an average yearly increase of 3%. Breeding sites that
had trained personnel (i.e., nestwatchers) stationed at active nests to
mitigate human disturbance had 28% higher reproductive output than nests
without this protection. Uncertainty around population trends was high,
but scenarios that continued the nestwatcher program were less likely to
predict abundance declines than scenarios without nestwatchers. Here,
the IPM-PVA framework provides a useful tool both for estimating the
effectiveness of past management actions and for exploring the
management needs of a delisted population, highlighting that continued
management action may be necessary to maintain population viability even
after meeting certain recovery criteria.
Description of the files:
These tables are a subset of data collected on bald eagles
(Haliaeetus leucocephalus) between 1987 and 2022 in Arizona,
USA. Data were collected by Arizona Game and Fish Department and their
partners.
cappello_baldeagleipm.R
ipm & pva code
data_mr.csv
data used in the mark-resight-recovery submodel
EagleID = Unique identifier for each banded eagle included in the
mark-recapture-recovery submodel
1987-2022 = For each year, a code (1-13) is given to represent the
observed state of each individual. State definitions are given in the
model code and manuscript text
data_abun.csv
data used in the abundance submodel
Year = Calendar year
OccupiedNestCount = Total number of occupied nesting territories found
in Arizona, USA during surveys between January and June each year
data_prod.csv
data used in the nest productivity submodel
Year = Calendar year
BANumber = Unique identifier for each nesting territory
NumFledged = Number of nestlings that fledged from each occupied nesting
territory in a given year. Ranges from 0 to 3.
eagle_constants.rds
list of model constants
nbrood = total number of occupied nests
nsites_prod = number of monitored nesting territories
nyear_prod = number of years in the productivity dataset
NW_prod = binary representing whether a nesting territory had
nestwatchers (1) or not (0) in that year
propNW = average proportion of nests that had nestwatchers from 1993 to
2022
propNW_t = proportion of nests that had nestwatchers in each year from
1993 to 2022
closures = binary representing whether a nesting territory had an area
closure (1) or not (0) in that year
propClos = average proportion of nests that had a closure from 1993 to
2022
propClos_t = proportion of nests that had a closure in each year from
1993 to 2022
yrID_prod = index of year corresponding to each row in the productivity
dataset
siteID_prod = index of nesting territory ID corresponding to each row in
the productivity dataset
first = first year that an individual was observed
first_state = first state that an individual was observed in
sex = sex of the individual: male (1) or female (0)
nyears_mr = number of years in the mark-resight-recovery dataset
nind = number of individuals in the mark-resight-recovery dataset
nyears = number of years in the abundance dataset
sex_ratio = number by which to divide productivity, to account for the
skewed sex ratio at fledging
nyears_proj = number of years projected forward in the PVA
scenarios = number of management scenarios tested in the PVA