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values in Crevalle jacks found in south Florida and in other species associated with
areas of restricted circulation.
Anti-fouling agents
In the past decade, some non-traditional contaminants have also been reported
in the vicinity of BNP. Organotin (TBTs) related antifouling compounds were reported in
sediments at the North Canal at Homestead Bayfront Marina and Irgarol 1051, an
antifouling booster biocide, has also been reported in many marinas in the bay. All
these pollutants are related only to boating activity and transport beyond their localized
usage area is not expected. Since TBTs have been banned, Irgarol 1051, in conjunction
with copper are contaminants that need to be further monitored with respect to marinas
and boatyards. Maxey (2006) analyzed surface water, seagrass, and sediment for the
antifouling biocide Irgarol 1051 and its metabolites. Concentrations of Irgarol in surface
water and seagrass ranged from N.D. to 1239 ng/L and 2.35 ng/g to 225 ng/g,
respectively. Concentrations of Irgarol in sediments were negligible (< 10 ng/g).
Bioconcentration factors (BCF) are measurement of the ratio of the chemical
concentration in a marine organism compared to that of the surrounding water. BCFs
greater than 1000 are considered to be accumulative, while BCFs greater than 5000 are
considered highly accumulative. BCF values for Irgarol uptake into seagrass ranged
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from 60 to 31588. While Irgarol was found at the majority of the marinas sampled, no
Irgarol was found at any coral reef, the specie reported to be the most sensitive to
Irgarol.
PCBs and PAHs
Lang and coworkers (Lang et al., 2002) reported the abundance and atmospheric
deposition of a variety of organic contaminants, including polychlorinated biphenyls
(PCBs) and polycyclic aromatic hydrocarbons (PAHs), in the Miami metropolitan area.
PAHs are commonly present in many sediment samples but their concentrations are
relatively low and consistent with background levels in urbanized areas. Marinas,
however, represent a deviation of this observation and is common to see sediments in
canals and access areas to major marinas to have elevated concentrations of Total
PAHs. Litz et al. (2007) reported total PCBs (sigma 73PCBs) present in the highest
concentrations and 5 times higher in males dolphins with sighting histories in the
northern, metropolitan area of Biscayne Bay than males with sighting histories in the
southern, more rural area. All compound classes had higher concentrations in northern
animals than in southern and are also high as compared to other studies of estuarine
dolphins and may place these animals at risk of reproductive failure and decreased
immune function.
CLIMATE CHANGE
Increasing concentrations of greenhouse gases in the atmosphere (carbon dioxide,
methane and nitrous oxide) have been shown to be the primary cause of global
increase of surface temperatures (IPCC 2007; Karl, et al. 2009), leading to warming of
the oceans, melting of ice fields and glaciers, and diverse climatic effects, which for
south Florida entail a number of important issues (Table 5.1), such as: sea level rise,
changes in rainfall and evaporation patterns affecting the amount of available
freshwater and potentially causing prolonged droughts and/or flooding; saltwater
intrusion into the coastal aquifers and public water supply; reduction of coastal
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stormwater release capacity due to sea level rise (SLR); and changes in tropical storm
and hurricane activity with increased surge levels (Heimlich et al 2009; Obeysekera
2011)
Sea Level Rise
Because of the sensitivity of vegetation patterns to subtle elevation differences,
we can expect the coming sea level rise to have a profound effect on the Park’s
terrestrial vegetation. Landward (uphill) migration of mangrove is already occurring on
the mainland, partly due to anthropogenic changes to the coastal water delivery
systems or driven by sea level rise. Wanless (1984) showed the movement of the
intertidal zone upward at the Coral Gables Waterway, caused by a slight rise in sea
level during the latter half of the 20th Century. However, the current rate of rise is faster
and is expected to be the controlling factor on future patterns of terrestrial vegetation as
more and more of the low coastal margin of the Park becomes inundated by marine
waters. Coronado-Molina et al. (2003) suggested that mangroves on the mainland
shore may be better suited to keep up with the sea level rise than those on the Keys,
due to higher productivity. Harlem and Meeder (2008) showed that sea level rise of only
1 foot would inundate much of the shoreline of Biscayne National Park at high tide
which would alter salinity regimes in the coastal area drastically and favor the westward
(inland) migration of saltwater habitats.
One aspect of great concern is the release of sediment and its associated
nutrients and pollutants to the marine system as coastlines erode. There are large
amounts of the former locked up in coastal sediments which will enter the sea as waves
and increased currents attack the existing shore deposits. While moving sediments by
currents is a natural phenomenon and most benthic communities are adapted to some
amount of sedimentation, the loading potential from rapid sediment adjustments as sea
level rises can only be considered a negative impact on Bay and especially on
marine/reef ecosystems.
Ocean Acidification
Ocean acidification refers to the ongoing increase in acidity (lowering pH) of the
Earth's oceans, caused by the uptake anthropogenic carbon dioxide of (CO2) from the
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atmosphere. This pH reduction causes problems for marine organisms which use
carbonate molecules (aragonite or calcite) to construct hard body parts or protective
shells, skeletons, and tests. Included in the affected groups are molluscs, foraminifera,
coccolithophores, crustaceans, starfish, bryozoans, and corals. Octocorals (soft corals)
and other marine organisms use calcite for structural support and scleractinian corals
use aragonite which is the metastable form of calcium carbonate used to build
skeletons. The Park lies in an area that will be least affected by acidification if the
models hold true (Guinotte et al. 2006), however, changes in the deep reefs seaward of
the Park should be expected in the near term and effects will increase in shallower
waters after 2100.
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Table 5.1 - Summary of Climate Change Impacts on Southeast Florida’s Water Resources
(Heimlich et al., 2009)
Climate change Potential threats to Potential threats of Other effects
impact fresh water supply severe flooding
Sea level rise • Saltwater intrusion of aquifer • Compromised stormwater • Barrier islands subject to
• Inundation of Southernmost drainage systems inundation and washout
Everglades with seawater • Reduced capacity of canals • Beach erosion
potentially affecting the and coastal control structures. • Coastal wetlands and
Biscayne Aquifer in south • Greater potential for flooding southernmost Everglades
Miami-Dade. due to heavy rain storms and encroachment
• Reduced groundwater flow hurricanes