This
dataset is a component of habitat connectivity analyses for Greater Sage-grouse
(GSG) in southeastern and central Oregon conducted in 2014 in accord with the
Sage Grouse Conservation Partnership (SageCon) by The Nature Conservancy in
Oregon (TNC) – see Jones (2015). Spanning the SageCon Assessment Area within
Oregon plus a 10-mile buffer, the data comprise least-cost paths (LCPs)
relating to the structural connectivity, or ‘continuity’, of sage-grouse
habitat amid the network of habitat patches defined by the ‘lek kernels’
dataset (the nodes of the analysis network).
Each LCP identifies the single-cell wide route of least cumulative
resistance for a sage grouse moving between a given pair of adjacent lek
kernels.
Least-cost
paths were identified and mapped with the Linkage Mapper toolset (McRae and
Kavanagh 2011) using for inputs the lek kernels data and the cost-weighted
distance (CWD) surface.
Linkage statistics yielded by Linkage Mapper were then used to characterize the
relative ‘quality’ and ‘robustness’ of each LCP.
In context of the broader
analysis, LCPs serve both as discrete representations of linkages between
adjacent pairs in the lek kernel network and as a conceptual basis for
least-cost corridors. LCPs and corridors
derive from the spatial configuration and continuity of habitat in the study
landscape. While they depict modeled routes of least cumulative resistance,
neither necessarily correlate with known routes of sage-grouse migration nor
describe the likelihood of particular routes attempted by individuals.
The least-cost approach to
modeling connectivity serves to complement the study’s circuit theoretic
component in several respects. First, delineation of LCPs provides an intuitive
and distinct visualization of the full analysis network. Second, metrics of
linkage ‘quality’ and ‘robustness’ (combined in this study into a single
metric; see ‘Linkage Statistics’) enable distinct comparison between linkages
as represented by the LCPs. Third, corridors demarcate broad belts of land with
relatively greater habitat continuity; such
‘linkage zones’ are useful for framing potential conservation actions
and for constraining models based in circuit theory.
METHODS
Using Linkage
Mapper, a preliminary network of lek kernels (n = 362) was constructed in which
linked kernel pairs were defined by adjacency in either Euclidean or
cost-weighted space. Minimum accumulated CWDs were calculated between each lek
kernel pair, and an LCP mapped for each linkage with the exclusion of those
that would intersect an intermediate lek kernel (n = 964).
Network Refinement
The initial analysis
network of lek kernels and associated LCPs resulted in a large set of linkage
corridors with extensive overlap, making it difficult to proceed with analyses
and interpretation. Consequently, a decision was made to further refine the
network prior to continuing with the analyses.
With guidance from
the Advisory Team, a ruleset was devised to hone the lek kernel network to
remove potential linkages of relatively low importance and facilitate
interpretation of the remaining individual linkage zones.
Network refinement
began with the application of an appropriate threshold CWD value over which
LCPs would be removed; this threshold was determined through iterative
modification of maximum CWD values with visual review of the resulting networks.
Based on the Advisory Team’s recommendations, all LCPs of > 120 cw-km were
removed with the exception of three required to maintain a minimum of two
linkages for every lek kernel (n = 54); this latter ‘path redundancy rule’was
adopted so as to support analysis of at least one alternative movement route
with the effective loss of any linkage to fire or other disturbance event.
Second, a few linkages (n = 3) were reinstated into the analysis set.
Next, network
constellations determined to be presently well-connected were removed from the
full analysis network. These linkages (n = 647) and associated lek kernels (n =
149) were first classified as either ‘internal’or ‘external’. Internal linkages
(n = 426) were defined as those connecting two lek kernels within the same core
area or BBD area and the associated lek kernels (n = 122) defined as those
connected only by internal linkages. External linkages (n
= 221) were defined as those < 90 cw-km and < 11.3 (Euclidean) km in
length, the latter equal to the mean plus one standard deviation of
straightline distances (km) measured edge-to-edge between all lek kernel pairs
within any single core area. The associated external lek kernels (n = 27) were
defined as those connected only by ‘internal’linkages and/or linkages < 90
cw-km and < 11.3 km.
Linkage Statistics
To better inform
comparisons between linkages in the refined analysis network (263 LCPs and 213
lek kernels) for conservation planning, statistics for each linkage were used
to derive two linkage metrics and, in turn, a single composite linkage index.
The first metric, a
measure of linkage ‘quality,’was based inversely on the ‘CWD to Path Length
Ratio’, the total cumulative cost along an LCP divided by the Euclidean
distance along the same path. This statistic, independent of LCP length, is a
measure of the average resistance encountered along an LCP.
The second metric,
interpreted as a measure of linkage ‘robustness’, stems from the ‘CWD to
Effective Resistance Ratio’. The ‘effective resistance’statistic, calculated
using Circuitscape within defined ‘linkage zones’, serves as a measure of the
relative isolation of lek kernels that accounts for the availability of
multiple movement routes. The ‘CWD to Effective Resistance Ratio,’in turn, can
be understood as a measure of average corridor width, the availability of
multiple, low-resistance routes within a corridor, and –by extension –the
‘robustness’of the linkage to being severed.
Raw statistic values
from LCPs were standardized from 0 –1 to constitute each linkage metric and the
metrics then multiplied to produce the ‘linkage index’.
The result served as
an integrated measure of both linkage quality and average corridor width;
higher values indicate stronger support for more focused consideration of protective
conservation action in the linkage at finer scales. Conversely, lower values
suggest poor quality and/or tenuous connections where restoration actions may
be warranted when considered with the priorities of decision makers.
While
the linkage index derives both from a statistic defined at scale the of a
single-cell width (LCPs ) and a statistics defined at the scale of the linkage
zones, the index was mapped to cells (LCPs) for the sake of greater visual
clarity when superimposed over raster model outputs.