text
stringlengths 0
6.44k
|
---|
Bufo marinus Cane toad
|
Cactoblastis cactorum Cactus moth
|
Canis familiaris Feral domestic dog
|
Ctenosaura similis Spiny tail iguana
|
Hemidactylus garnotti Indo-Pacific gecko
|
Hemidactylus mabouia Tropical gecko
|
Felis catus Feral domestic cat
|
Iguana iguana Green iguana
|
Mus musculus House mouse
|
Musca domestica House fly
|
Osteopilus serpentrionalis Cuban treefrog
|
Paratachardina lobata lobata Lobate lac scale
|
Psittacidae family Parrots and parakeets
|
Rattus rattus Black rat
|
Ramphotyphlops braminus Brahminy blind snake
|
Saissetia coffeae Hemispherical scale
|
Solenopsis invicta Red imported fire ant
|
Sturnus vulgaris European starling
|
Zachrysia provisoria Cuban tree snail
|
EEL Program, Management Plan, Part II – Pine Rockland (DRAFT) _____________________________________________________________________________________________________________________
|
Page 27
|
tree cavities, such as woodpeckers, also make pine rocklands more susceptible to damage
|
from these birds. Starlings not only compete with the native birds for tree cavities, but have
|
even been observed evicting woodpeckers from their nests to claim the cavity for their own
|
(Stevenson and Anderson 1994).
|
• Parrots and parakeets – Over twenty species of parrots and parakeets have been observed
|
nesting in the wild in South Florida (FWC 2007). Due to their flocking behavior and more
|
aggressive mannerisms, they out-compete native birds for both food and space, claiming
|
fruits, nuts and tree cavities for themselves (Taylor et al. 2004). In addition, they contribute
|
to the spread of exotic plants through seed dispersal (Snyder et al. 1990). While members of
|
this family occur in many South Florida habitats, the previously mentioned habits make them
|
particularly harmful in pine rocklands where there is a high concentration of native bird
|
species that depend upon tree cavities and where management of exotic plants is already
|
challenging due to complications related to burning.
|
• Lobate lac scale - The lobate lac scale, a scale insect that is native to India and Sri Lanka,
|
was found in Broward County in 1999, and has since become widespread in southern Florida.
|
The species belongs to the lac scale family, Kerriidae, the best-known species of which is the
|
true lac scale insect. The lobate lac scale has been found mostly on woody dicotyledonous
|
plants. It infests the woody portions of twigs and small branches and less frequently main
|
stems under one inch in diameter. It not usually found on branches or main stems greater
|
than approximately one inch in diameter. It has not been observed on foliage. Some woody
|
plant species appear to be highly susceptible, including certain natives, e.g., wax-myrtle,
|
cocoplum, buttonwood, strangler-fig, myrsine, bay species, and wild-coffee. Lobate lac scale
|
is more commonly known for its damage to hammock systems, but it is also a concern in
|
pine rocklands due to its preference for certain rare bushes, particularly Florida prairieclover
|
and crenulate leadplant.
|
3.11 Other Problem Species
|
Many native plant species can be considered problem species in pine rocklands. Some native
|
species become aggressive and can out-compete other native species when artificial habitat
|
changes occur, such as drainage, intense fires, or fire suppression. While these species are native,
|
control efforts should still be used when required to maintain desirable ecosystem structure and
|
composition. Problem species include cabbage palm, muscadine grape, southern sumac, lacy
|
bracken fern, and earleaf greenbrier.
|
In addition to the above species, all native hardwoods can be considered problem species in the
|
absence of fire. Common hardwoods include live oak, poisonwood, and myrsine.
|
Two native plant species that occur in pine rocklands commonly cause dermatitis in sensitive
|
people. These are poisonwood and poison-ivy. Both are common pine rockland species. Lower
|
densities of both can be achieved by proper management of pine rocklands. Densities of both,
|
especially poisonwood, can increase dramatically with fire suppression.
|
EEL Program, Management Plan, Part II – Pine Rockland (DRAFT) _____________________________________________________________________________________________________________________
|
Page 28
|
3.12 Pollutants
|
Although there are innumerable types of pollutants that could potentially affect EEL pine
|
rockland sites, the primary sources of concern are dumping, mosquito spraying, pesticides
|
(insecticides, herbicides, fungicides, miticides, nematicides), nutrients, sediments, animal wastes,
|
miscellaneous household and industrial chemical wastes, and wind-blown debris. Please refer to
|
Part I, Section 5.2.5 of this management plan for details about these potential threats.
|
3.13 Cultural Resources
|
The potential exists for the presence of Native American artifacts in pine rocklands because
|
small game hunting would likely have occurred in such wooded areas and close to rivers. The
|
pineland’s higher ground would help protect populations from hurricane-related storm surges.
|
There would not, however, likely be a higher probability of evidence of indigenous groups in
|
pine rocklands than in hammocks or coastal areas.
|
EEL Program, Management Plan, Part II – Pine Rockland (DRAFT) _____________________________________________________________________________________________________________________
|
Page 29
|
4.0 Management Issues
|
This section describes the most important issues that require attention for the successful
|
management of pine rockland sites. While drafting these guidelines the team paid attention to the
|
main goals outlined for pine rockland habitat by the Miami-Dade County Natural Areas
|
Management Plan (DERM 1995, USFWS 2000).
|
4.1 Acquisition Needs for Remaining Pine Rockland Fragments
|
There are few remaining pine rockland fragments in Miami-Dade County that are suitable for
|
acquisition. Every attempt should be made by the EEL program to acquire any of these
|
remaining pine rocklands before they are developed. However, prior to attempting acquisition
|
each site must individually be approved by the Board of County Commissioners for acquisition
|
and funding must be in place. Finally, the seller must be willing to sell the property.
|
The largest of these fragments occur in the Richmond Pine Rocklands surrounding Miami
|
Metrozoo. There are two preserved pine rockland areas here, Larry & Penny Thompson Park and
|
Martinez Pineland, both owned by the Parks and Recreation Department. Negotiations are
|
currently underway for the EEL program to begin management of pine rockland at Miami
|
Metrozoo. There are other areas of high-quality pine rockland, many with populations of
|
endangered species, that are suitable for EEL acquisition. These include properties owned by the
|
University of Miami, U.S. Coast Guard, and Department of Defense.
|
Other owners of significant pine rockland areas in Miami-Dade County include the Miami-Dade
|
County School Board, Retreat Construction Corp, Barbara Hampson-Keller, and several other
|
private owners. Some of these are probably unwilling sellers.
|
Some of the pine rockland fragments that are suitable for acquisition are listed in Table 5.
|
Table 5: Pine rockland fragments suitable for acquisition in Miami-Dade County.
|
Sites currently listed by the EEL program are marked with an asterisk (*)
|
Property Name
|
Subsets and Splits
No community queries yet
The top public SQL queries from the community will appear here once available.