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woodpecker |
Sandhill |
bird index |
CLIP |
P1 |
CLIP |
P2 |
CLIP |
P1 |
CLIP |
P2 |
CLIP |
P1 |
CLIP |
P2 |
CLIP |
P1 |
CLIP |
P2 |
CLIP |
P1 |
CLIP |
P2 |
CLIP |
P1 |
CLIP |
P2 |
CLIP |
P1 |
CLIP |
P2 |
Baseline area of target (km2 |
) 5,101.0 260.6 3,978.1 99.1 4,438.8 215.1 3,527.6 n/a 3,895.5 35.1 2,652.7 131.5 4,838.8 229.9 |
Area (km2 |
) |
2040 Urban Int SLR 4,999.1 246.8 3,977.9 99.1 4,395.4 209.0 3,523.7 n/a 3,803.5 29.4 2,612.0 125.5 4,741.0 217.4 |
2040 Urban High SLR 4,998.1 246.8 3,977.2 99.1 4,395.0 209.0 3,523.5 n/a 3,803.3 29.4 2,611.9 125.5 4,740.4 217.4 |
2070 Alt Urban Int SLR 4,859.9 229.0 3,977.4 99.1 4,304.0 196.9 3,516.8 n/a 3,681.1 26.1 2,541.2 117.3 4,608.7 201.7 |
2070 Alt Urban High SLR 4,850.4 228.8 3,969.7 99.0 4,300.0 196.8 3,515.6 n/a 3,677.5 26.1 2,540.6 117.3 4,601.4 201.6 |
2070 Trend Urban Int SLR 4,711.1 220.6 3,977.1 99.1 4,219.0 190.0 3,459.1 n/a 3,555.8 25.2 2,498.8 111.6 4,466.7 194.5 |
2070 Trend Urban High SLR 4,701.7 220.4 3,969.4 99.0 4,215.1 190.0 3,458.0 n/a 3,552.3 25.2 2,498.2 111.6 4,459.5 194.3 |
% decrease from baseline |
2040 Urban Int SLR 2.0 5.3 0.004 0.003 1.0 2.9 0.1 n/a 2.4 16.4 1.5 4.6 2.0 5.4 |
2040 Urban High SLR 2.0 5.3 0.02 0.01 1.0 2.9 0.1 n/a 2.4 16.4 1.5 4.6 2.0 5.4 |
2070 Alt Urban Int SLR 4.7 12.1 0.02 0.01 3.0 8.5 0.3 n/a 5.5 25.5 4.2 10.8 4.8 12.3 |
2070 Alt Urban High SLR 4.9 12.2 0.2 0.1 3.1 8.5 0.3 n/a 5.6 25.6 4.2 10.8 4.9 12.3 |
2070 Trend Urban Int SLR 7.6 15.3 0.02 0.01 5.0 11.7 1.9 n/a 8.7 28.1 5.8 15.2 7.7 15.4 |
2070 Trend Urban High SLR 7.8 15.4 0.2 0.1 5.0 11.7 2.0 n/a 8.8 28.2 5.8 15.2 7.8 15.5 |
n/a ¼ not applicable. |
Figure 2. Study objective was to model susceptibility |
scenarios resulting from urbanization and sea level rise (SLR) |
to understand their potential future impacts on the Peninsular |
Florida Landscape Conservation Cooperative conservation |
targets, completed in 2018. Difference in the percent of area |
lost (of Critical Lands and Waters Identification Project Priority |
1 and 2 combined) between SLR scenarios (High and |
Intermediate [Int]), holding urbanization scenarios constant |
for High Pine & Scrub (HPS), Coastal Uplands (CU), and |
Freshwater Aquatics (FA) Priority Resources. Higher values |
indicate a greater difference in the percent area lost between |
High and Intermediate SLR. |
Impacts of Urbanization and Sea Level Rise S.S. Romanach et al. ˜ |
Journal of Fish and Wildlife Management | www.fwspubs.org June 2020 | Volume 11 | Issue 1 | 178 |
Downloaded from http://meridian.allenpress.com/jfwm/article-pdf/11/1/174/3103287/i1944-687x-11-1-174.pdf by guest on 29 February 2024 |
Table 3. Study objective was to model susceptibility scenarios resulting from urbanization and sea level rise (SLR) to understand |
their potential future impacts on the Peninsular Florida Landscape Conservation Cooperative conservation targets, completed in |
2018. The area (km2 |
) and percent (%) decrease in area of each model input (i.e., conservation target) for the Coastal Uplands Priority |
Resource for each future model scenario of urbanization (Urban) and SLR. The baseline area of target represents the current extent |
of the input model data with the 2010 urban baseline extracted. Each area and percent decrease in area is represented for Critical |
Lands and Waters Identification Project Priority 1 and 2 (CLIP P1 and CLIP P2, respectively). The CLIP Landscape Integrity Index values |
8 (high ecological integrity) and Florida Ecological Greenways Network Priority 1 (P1 ¼ Critical Linkages) were used for |
calculations. We also present the area and percent change in area for the entire Coastal Uplands Priority Resource for CLIP P1 and |
CLIP P2. |
Model data and scenario |
Coastal |
Uplands |
Priority |
Resource |
Protected |
status |
Landscape |
Integrity |
(8) |
Ecological |
Greenways |
(P1) |
American |
oystercatcher |
Snowy |
plover |
CLIP |
P1 |
CLIP |
P2 |
CLIP |
P1 |
CLIP |
P2 |
CLIP |
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