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Uplands (mean difference for all urbanization scenarios ¼ |
15.03) compared with High Pine and Scrub (mean¼0.13) |
and Freshwater Aquatics (mean¼0.07). Furthermore, the |
difference in percent area lost between high and |
intermediate SLR for Coastal Uplands is slightly greater |
under the Alternative development scenario (21.12) than |
under the Trend development scenario (20.83). |
Discussion |
Our results project increasing losses in extent and area |
of priority conservation ecosystems moving toward |
2070. These findings are attributable to projections of |
increasing urbanization and SLR over the coming |
decades. Generally, we found that the greatest losses |
are projected to be from SLR than urbanization, although |
largely from impacts to Coastal Uplands. The increase in |
percent area lost from Coastal Uplands between high |
and intermediate SLR is projected to be slightly greater |
under Alternative urbanization than Trend. This difference is potentially because Alternative aims to reduce |
sprawl; therefore, more habitat remains compared with |
Trend, and this remaining habitat can be impacted by |
high SLR. |
Florida has experienced many negative impacts from |
urban development, including destruction and loss of |
important habitats and ecosystem services such as flood |
risk reduction (Arnold and Gibbons 1996). Florida had a |
mandate to limit urban sprawl and minimize negative |
impacts on the natural environment (Local Government |
Comprehensive Planning and Land Development Regulation Act of 1985; Frank 1985) but even so, policies were |
not always adopted at the local level (Brody and |
Highfield 2005). To protect the environment and restore |
environmental damage caused by urbanization, Florida |
enables several options for landowners and developers, |
such as establishing conservation easements where |
landowners are paid not to develop land in exchange |
for reduced taxation or creation of mitigation banks |
(where the land is used to offset continued development |
elsewhere). Brody and Highfield (2005) suggest that |
imposing legal or financial consequences for not |
adhering to urban planning requirements could lead to |
greater compliance. In the meantime, scientists, citizens, |
natural resource managers, and urban planners are |
increasingly required to innovate alternative solutions |
to help with the conservation of critical habitats and |
ecosystems of concern. |
For High Pine and Scrub, the projection is for |
urbanization to cause greater losses than SLR. We found |
a trend of greater percentage of area projected to be lost |
for the gopher tortoise and the Sandhill bird index |
(brown-headed nuthatch, northern bobwhite, Bachman’s |
sparrow), indicating that these species may be particularly vulnerable to future urbanization. Urbanization has |
resulted in a greater than 60% reduction in scrub habitat |
in Florida (Richardson 1989). These areas provide habitat |
for hundreds of species, many of which are endangered |
(U.S. Endangered Species Act; ESA 1973, as amended). |
Gopher tortoise populations, for example, have declined |
by 80% in the past century due to urbanization and |
other human development activities that have destroyed |
their habitat (Diemer 1986). Although managers have |
developed methods that can support gopher tortoise |
populations even with dramatically reduced important |
habitat, for example, by reinstituting summer and winter |
prescribed burns (Landers and Speake 1980; Russell et al. |
1999), these restoration actions are difficult to implement as urbanization and infrastructure encroach on |
remaining important habitat. Pickens et al. (2017) |
showed that fire suppression due to urban encroachment was most likely to impact habitat restoration for |
Backman’s sparrow. Low-density urban growth (the |
Trend scenario) has a disproportionate negative impact, |
per capita, on these species. |
Projections suggest that losses for Freshwater Aquatics from urbanization and SLR will be minimal. One |
explanation is that freshwater has less potential for |
impact from SLR because of greater distances from the |
coast and less potential impact from urbanization owing |
to the challenges of developing on water bodies such as |
natural lakes, rivers, and streams. The persistence of |
freshwater wetland ecosystems depends on their ability |
to keep pace with SLR through soil accretion (Scavia et |
al. 2002). However, one aspect that our SLR scenarios do |
not consider is saltwater intrusion into the aquifer. If |
saltwater intrusion were to carry far into freshwater |
ecosystems, many of the species that inhabit those |
ecosystems may not be able to persist (e.g., Nielsen et al. |
2003). Depending on hydrologic conditions, saltwater |
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 | 180 |
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 |
intrusion from SLR may range from a few meters to more |
than a kilometer (Werner and Simmons 2009). Much of |
Florida has a porous, limestone base, and most of the |
state is lower than 3.7 m in elevation, with most saltintolerant communities occurring at less than a 2-m |
elevation (Saha et al. 2011). In addition, any location in |
Florida is a maximum of 100 km from the coast, with |
most locations much more proximal to the state’s |
extensive coastline; therefore, saltwater intrusion requires serious consideration both for the natural world |
and for human needs. |
With losses up to 46.8% for Coastal Uplands, this lowlying Priority Resource is the most vulnerable to SLR, |
which is significant because of its importance for |
Florida’s tourism industry. These coastal ecosystems |
would benefit from sustainable management to continue to attract tourists that contribute to Florida’s |
economy. The Florida Keys alone (Figure 1) represent a |
multibillion-dollar tourist industry including diving, |
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