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SFWSC_005
Seasonal Electrofishing Data from Rookery Branch and Tarpon Bay, Everglades National Park from November 2004 to Present
Dr.
Jennifer
Rehage
Southeast Environmental Research Center and South Florida Water, Sustainability, and Climate Project
Principle investigator
Florida International University
University Park
ECS 119
Miami
FL
33199
USA
305-348-0181
rehagej@fiu.edu
Florida Coastal Everglades LTER Program
Florida International University
University Park
OE 148
Miami
FL
33199
USA
305-348-6054
fcelter@fiu.edu
http://fcelter.fiu.edu
Jennifer
Rehage
Southeast Environmental Research Center and South Florida Water, Sustainability, and Climate Project
Florida International University
University Park
ECS 119
Miami
FL
33199
USA
305-348-0181
rehagej@fiu.edu
http://www.fiu.edu/~envstud/index_environment.html
Principal Investigator
2020-10-01
This study examines temporal and spatial dynamics in the fish community of the oligohaline to mesohaline reaches of ecotonal creeks along the southwest region of Everglades National Park. Collections of fish in SW ENP during 2004 - 2014 across Rookery Branch and Tarpon Bay. Sampling started in the wet season of 2004, and has been conducted three times per year at these approximate times: November (wet season); February (transition); and April (dry season). Electrofishing samples were processed in the field, and all species (except for non-natives) were returned live at the point of collection. In the Rookery Branch region, fish abundance varies markedly yearly and seasonally. Catches peak in the drier months, reflecting a pulse of movement by freshwater taxa into creeks as marshes upstream dry. The timing of this pulse is closely tied to the pattern of water recession in upstream marshes, and has important ramifications for wading bird prey availability.
SFWSC
South Florida Water, Sustainability, and Climate Project
ecological research
long-term monitoring
consumer dynamics
fishes
Rookery Branch
Electrofishing
Everglades National Park
catches
consumers
freshwater
estuarine
biology
species
wet
dry
transitional
salinity
catch per unit effort
prey fish
preditors
dissolved oxygen
water temperature
seasonality
species
climate
South Florida
hydro-economic models
management schemes
impact
economic value
ecosystem services
climate variability
climate change
sea level rise
adaptive water management
economic productivity
LTER Keyword Thesaurus
These data are classified as 'Type II' whereby original SFWSC experimental data collected by individual SFWSC researchers are to be released to restricted audiences according to terms specified by the owners of the data. Type II data are considered to be exceptional and should be rare in occurrence. The justification for exceptions must be well documented and approved by the lead PI and Site Data Manager. Some examples of Type II data restrictions may include: locations of rare or endangered species, data that are covered under prior licensing or copyright (e.g., SPOT satellite data), or covered by the Human Subjects Act, Student Dissertation data and those data related to the SFWSC project but not funded by the National Science Foundation (NSF) WSC program (EAR-1204762) and the NIFA Award Number 2012-67003-19862. Researchers that make use of Type II Data may be subject to additional restrictions to protect any applicable commercial or confidentiality interests. For a complete description of the SFWSC Data Distribution and Data User Agreement, please go to SFWSC Data Management Policy: http://eimc.fiu.edu/projects/SFWSC/SFWSC_DataManagementPolicy.pdf. Additionally, two copies of the manuscript must be submitted to the South Florida Water, Sustainability and Climate Project, c/o Dr. Mike Sukop, Department of Earth & Environment, Florida International University, ECS 347, 11200 SW 8th Street, Miami, Florida 33199.
The Study Extent of this dataset includes areas near FCE Shark River Slough research sites (downstream of SRS 3) from Rookery Branch to Tarpon Bay within Everglades National Park, South Florida also includes South Florida Water, Sustainability, and Climate Project Study Area.
-81.078
-81.078
25.365
25.365
Florida Coastal Everglades LTER Study Area: South Florida, Everglades National Park, and Florida Bay
-81.078
-80.490
25.761
24.913
2004-11-01
2014-05-05
species
Fundulus confluentus
species
Fundulus chrysotus
species
Notemigonus crysoleucas
species
Esox americanus
species
Lepomis sp.
species
Erimyzon sucetta
species
Fundulus seminolis
species
Noturus gyrinus
species
Lepomis gulosus
species
Lepomis macrochirus
species
Lepomis microlophus
species
Lepomis punctatus
species
Lepomis marginatus
species
Enneacanthus gloriosus
species
Esox niger
species
Lepisosteus platyrhincus
species
Micropterus salmoides
species
Amia calva
species
Centropomus undecimalis
species
Megalops atlanticus
species
Anguilla rostrata
species
Ariopsis felis
species
Lutjanus griseus
species
Bagre marinus
species
Carcharhinus leucas
species
Sciaenops ocellatus
species
Caranx hippos
species
Eucinostomus gula
species
Trinectes maculatus
species
Anchoa mitchilli
species
Microgobius gulosus
species
Lophogobius cyprinoides
species
Fundulus grandis
species
Strongylura sp.
species
Lagodon rhomboides
species
Archosargus probatocephalus
species
Eugerres plumieri
species
Kleptolebias marmoratus
species
Eucinostomus harengulus
species
Cynoscion nebulosus
species
Gobiosoma robustrum
species
Mugil cephalus
species
Callinectes sapidus
species
Eucunostomus sp
species
Elops saurus
species
Gobiosoma sp
species
Clarias batrachus
species
Tilapia mariae
species
Oreochromis aureus
species
Cichlasoma urophthalmus
species
Belonesox belizanus
species
Hemichromis letourneuxi
species
Pterygoplichthys multiradiatus
species
Macrognathus siamensis
This is a short-term electrofishing dataset and subsequent data will be appended if necessary.
Jennifer
Rehage
Southeast Environmental Research Center and South Florida Water, Sustainability, and Climate Project
Principal Investigator
Florida International University
University Park
ECS 337
Miami
FL
33199
USA
305-348-0181
rehagej@fiu.edu
Principal Investigator
http://www.fiu.edu/~envstud/index_environment.html
South Florida Water, Sustainability, and Climate Project
Dr. Mike Sukop
Florida International University
University Park
ECS 347
11200 SW 8th Street
Miami
FL
33199
USA
305-348-3117
305-348-3877
sukopm@fiu.edu
http://sfwsc.fiu.edu/index.html
Florida Coastal Everglades LTER Program
Florida International University
University Park
OE 148
Miami
FL
33199
USA
305-348-6054
fcelter@fiu.edu
http://fcelter.fiu.edu
Fish were collected via electrofishing methods,
No free lunch: displaced marsh consumers regulate a prey subsidy to an estuarine consumer.
Ross
E
Boucek
2013-10-01
Oikos
122
10
1453-1464
Electrofishing
Dr.
Jennifer
Rehage
2004-01-01
Sampling is conducted at 15 mangrove creeks in two drainages: Rookery Branch and the North, Roberts, and Watson rivers. Electrofishing is used to target large-bodied predatory species. At each creek, we systematically sample, three 100 meter long sections of creek bank by electrofishing (0-100m, 200-300m, and 400-500m). Each electrofishing bout lasts five minutes (pedal time). Electrofishing is an effective method for sampling large fishes in freshwater habitats, and eletrofishing catch per unit effort (CPUE) provides a reliable index of fish abundance. For all bouts, electrofishing power is standardized to 1500 watts according to the ambient temperature and conductivity conditions. Because creek width is considerably greater than the electric field generated by the electrofisher, a left or right bank was randomly selected for each bout. Folling USGS-NAWQA guidelines, all electrofishing is conducted using intermittent application of electrical current to prevent fish from fleeing deep beneath the mangroves. All fish captured are placed in a holding tank, identified, measured (to the nearest 1-mm standard or total length), weighed (if necessary), and released after full recovery. We measure mass of those species for wich we do not have reliable length-mass regression equations with which to estimate mass-this procedure results in less handling of fishes and reduces stress on the specimens. Only non-indigenous species are saved and preserved in 10 percent formalin to be returned to the laboratory for processing. Although electrofishing typically targets large fish species, we routinely capture specimens as small as 5-cm standard length (SL). During each sampling event, we use a YSI 85 unit to record physico-chemical parameters (water temperature, specific conductance/salinity, and dissolved oxygen) at the beginning of each electrofishing bout. Water clarity and bottom type are measured with a measuring stick and turbidity with an electronic turbidity meter.
Sampling is conducted at 15 mangrove creeks in two drainages: Rookery Branch and the North, Roberts, and Watson rivers. Electrofishing is used to target large-bodied predatory species. At each creek, we systematically sample, three 100 meter long sections of creek bank by electrofishing (0-100m, 200-300m, and 400-500m). Each electrofishing bout lasts five minutes (pedal time). Electrofishing is an effective method for sampling large fishes in freshwater habitats, and eletrofishing catch per unit effort (CPUE) provides a reliable index of fish abundance. For all bouts, electrofishing power is standardized to 1500 watts according to the ambient temperature and conductivity conditions. Because creek width is considerably greater than the electric field generated by the electrofisher, a left or right bank was randomly selected for each bout. Folling USGS-NAWQA guidelines, all electrofishing is conducted using intermittent application of electrical current to prevent fish from fleeing deep beneath the mangroves. All fish captured are placed in a holding tank, identified, measured (to the nearest 1-mm standard or total length), weighed (if necessary), and released after full recovery. We measure mass of those species for wich we do not have reliable length-mass regression equations with which to estimate mass-this procedure results in less handling of fishes and reduces stress on the specimens. Only non-indigenous species are saved and preserved in 10 percent formalin to be returned to the laboratory for processing. Although electrofishing typically targets large fish species, we routinely capture specimens as small as 5-cm standard length (SL). During each sampling event, we use a YSI 85 unit to record physico-chemical parameters (water temperature, specific conductance/salinity, and dissolved oxygen) at the beginning of each electrofishing bout. Water clarity and bottom type are measured with a measuring stick and turbidity with an electronic turbidity meter.
Sampling is conducted at 15 mangrove creeks in two drainages: Rookery Branch and the North, Roberts, and Watson rivers. Electrofishing is used to target large-bodied predatory species. At each creek, we systematically sample, three 100 meter long sections of creek bank by electrofishing (0-100m, 200-300m, and 400-500m). Each electrofishing bout lasts five minutes (pedal time). Electrofishing is an effective method for sampling large fishes in freshwater habitats, and eletrofishing catch per unit effort (CPUE) provides a reliable index of fish abundance. For all bouts, electrofishing power is standardized to 1500 watts according to the ambient temperature and conductivity conditions. Because creek width is considerably greater than the electric field generated by the electrofisher, a left or right bank was randomly selected for each bout. Folling USGS-NAWQA guidelines, all electrofishing is conducted using intermittent application of electrical current to prevent fish from fleeing deep beneath the mangroves. All fish captured are placed in a holding tank, identified, measured (to the nearest 1-mm standard or total length), weighed (if necessary), and released after full recovery. We measure mass of those species for wich we do not have reliable length-mass regression equations with which to estimate mass-this procedure results in less handling of fishes and reduces stress on the specimens. Only non-indigenous species are saved and preserved in 10 percent formalin to be returned to the laboratory for processing. Although electrofishing typically targets large fish species, we routinely capture specimens as small as 5-cm standard length (SL). During each sampling event, we use a YSI 85 unit to record physico-chemical parameters (water temperature, specific conductance/salinity, and dissolved oxygen) at the beginning of each electrofishing bout. Water clarity and bottom type are measured with a measuring stick and turbidity with an electronic turbidity meter.
Electrofishing
fish capture
Apply electric current to sampling area
net immobilized fish
place fish into a water tank on boat
21' Aluminum boat fitted with a generator and other electrofishing equipment (see citation 28)
The Study Extent of this dataset includes areas near FCE Shark River Slough research sites (downstream of SRS 3 and upstream of SRS 4) from Rookery Branch within Everglades National Park, South Florida
Sampling is conducted at 15 mangrove creeks in two drainages: Rookery Branch and the North, Roberts, and Watson rivers. Electrofishing is used to target large-bodied predatory species. At each creek, we systematically sample, three 100 meter long sections of creek bank by electrofishing (0-100m, 200-300m, and 400-500m). Each electrofishing bout lasts five minutes (pedal time). Electrofishing is an effective method for sampling large fishes in freshwater habitats, and eletrofishing catch per unit effort (CPUE) provides a reliable index of fish abundance. For all bouts, electrofishing power is standardized to 1500 watts according to the ambient temperature and conductivity conditions. Because creek width is considerably greater than the electric field generated by the electrofisher, a left or right bank was randomly selected for each bout. Folling USGS-NAWQA guidelines, all electrofishing is conducted using intermittent application of electrical current to prevent fish from fleeing deep beneath the mangroves. All fish captured are placed in a holding tank, identified, measured (to the nearest 1-mm standard or total length), weighed (if necessary), and released after full recovery. Only non-indigenous species are saved and preserved in 10 percent formalin to be returned to the laboratory for processing. During each sampling event, we use a YSI 85 unit to record physico-chemical parameters (water temperature, specific conductance/salinity, and dissolved oxygen) at the beginning of each electrofishing bout. Water clarity and bottom type are measured with a measuring stick and turbidity with an electronic turbidity meter.
Rookery Branch 7
-80.897
-80.897
25.429
25.429
Rookery Branch 8
-80.872
-80.872
25.455
25.455
Rookery Branch 9
-80.862
-80.862
25.460
25.460
Rookery Branch 10
-80.865
-80.865
25.464
25.464
Rookery Branch 11
-80.876
-80.876
25.464
25.464
Rookery Branch 12
-80.916
-80.916
25.459
25.459
Rookery Branch 13
-80.89
-80.89
25.45
25.45
Rookery Branch 14
-80.92
-80.92
25.43
25.43
Rookery Branch 15
-80.95
-80.95
25.42
25.42
Rookery Branch 16
-80.94
-80.94
25.45
25.45
TB1
-80.97
-80.97
25.41
25.41
TB2
-80.97
-80.97
25.41
25.41
TB3
-80.98
-80.98
25.43
25.43
TB4
-80.97
-80.97
25.43
25.43
All data from sampling, catch, and processing datasheets are entered in spreadsheet format using Microsoft Excel. Separate files are created and managed for two sampling methods (electrofishing and minnow trapping). Since analyses are multiyear, all years of data are combined into a single file, and as new data is gathered, it is added to a master datafile containing all previous years of data. Post data entry, data are verified and validated by a different technician from the technician that entered the data. Then, the data files are cleaned and formatted for statistical analyses.
Florida Coastal Everglades LTER: Coastal Oligotrophic Ecosystems Research-the Coastal Everglades
Daniel
Childers
Florida Coastal Everglades LTER Program
Department of Biological Sciences
Florida International University
University Park
OE 167
Miami
FL
33199
USA
305-348-3101
305-348-1986
childers@fiu.edu
Lead Principal Investigator
Joseph
Boyer
Florida Coastal Everglades LTER Program
Southeast Environmental Research Center
Florida International University
University Park
OE 148
Miami
FL
33199
USA
305-348-4076
305-348-4096
Principal Investigator
James
Fourqurean
Florida Coastal Everglades LTER Program
Department of Biological Sciences
Florida International University
University Park
OE 167
Miami
FL
33199
USA
305-348-4084
305-348-4096
Principal Investigator
Rudolf
Jaffe
Florida Coastal Everglades LTER Program
Department of Chemistry
Florida International University
University Park
CP 304
Miami
FL
33199
USA
305-348-2456
305-348-4096
Principal Investigator
Joel
Trexler
Florida Coastal Everglades LTER Program
Department of Biological Sciences
Florida International University
University Park
OE 167
Miami
FL
33199
USA
305-348-1966
305-348-1986
Principal Investigator
We are investigating how variability in regional climate, freshwater inputs, disturbance, and perturbations affect the coastal Everglades ecosystem. Our long term research program focuses on testing the following central idea and hypotheses: Regional processes mediated by water flow control population and ecosystem level dynamics at any location within the coastal Everglades landscape. This phenomenon is best exemplified in the dynamics of an estuarine oligohaline zone where fresh water draining phosphorus-limited Everglades marshes mixes with water from the more nitrogen-limited coastal ocean. Hypothesis 1: In nutrient-poor coastal systems, long-term changes in the quantity or quality of organic matter inputs will exert strong and direct controls on estuarine productivity, because inorganic nutrients are at such low levels. Hypothesis 2: Interannual and long-term changes in freshwater flow controls the magnitude of nutrients and organic matter inputs to the estuarine zone, while ecological processes in the freshwater marsh and coastal ocean control the quality and characteristics of those inputs. Hypothesis 3: Long-term changes in freshwater flow (primarily manifest through management and Everglades restoration) will interact with long-term changes in the climatic and disturbance (sea level rise, hurricanes, fires) regimes to modify ecological pattern and process across coastal landscapes.
National Science Foundation under Grant # 9910514
The FCE LTER Project Study area is located in South Florida, mostly in Everglades National Park. There are a total of 21 sampling sites located in two major regions: 1) Shark River Slough and 2) Taylor Slough/Panhandle.
-81.078
-80.490
25.761
24.913
2000-05-01
2006-04-30
SFWSC_005
Seasonal Electrofishing Data from Rookery Branch and Tarpon Bay, Everglades National Park from November 2004 to Present
SFWSC_005
212
ASCII
1
\r\n
column
,
ID
Sampling ID
Sampling ID
nominal
Sampling ID
Year
Year
long term sampling year
ordinal
long term sampling year
DATE
date
Collection Date
datetime
YYYY-MM-DD
1
2004-11-15
2014-05-05
SEASON
season
Everglades Season
text
WET
wet season
DRY
dry season
TRANS
Transitional season
-9999
Value was not recorded
River
drainage site
drainage site
text
drainage site
Creek
drainage creek
drainage creek
code
drainage creek
SITETYPE
site type
type of sampling site
text
type of sampling site
BOUT
bout number
Electrofishing bout
code
Electrofishing bout
-9999
Value was not recorded
FUNCON4
species count
number of species 4
data
number
1
real
-9999
Value was not recorded
FUNCHR8
species count
number of species 8
data
number
1
real
-9999
Value was not recorded
NOTCRY9
species count
number of species 9
data
number
1
real
-9999
Value was not recorded
ESONIG14
species count
number of species 14
data
number
1
real
-9999
Value was not recorded
LEPPLA17
species count
number of species 17
data
number
1
real
-9999
Value was not recorded
ESOAME18
species count
number of species 18
data
number
1
real
-9999
Value was not recorded
LEPSPP19
species count
number of species 19
data
number
1
real
-9999
Value was not recorded
MCSAL20
species count
number of species 20
data
number
1
real
-9999
Value was not recorded
ERISUC33
species count
number of species 33
data
number
1
real
-9999
Value was not recorded
FUNSEM34
species count
number of species 34
data
number
1
real
-9999
Value was not recorded
EURGUL35
species count
number of species 35
data
number
1
real
-9999
Value was not recorded
TRIMAC36
species count
number of species 36
data
number
1
real
-9999
Value was not recorded
NOTGYR37
species count
number of species 37
data
number
1
real
-9999
Value was not recorded
LEPGUL38
species count
number of species 38
data
number
1
real
-9999
Value was not recorded
LEPMAC39
species count
number of species 39
data
number
1
real
-9999
Value was not recorded
LEPMIC40
species count
number of species 40
data
number
1
real
-9999
Value was not recorded
LEPPUN41
species count
number of species 41
data
number
1
real
-9999
Value was not recorded
LEPMAR42
species count
number of species 42
data
number
1
real
-9999
Value was not recorded
ENNGLO47
species count
number of species 47
data
number
1
real
-9999
Value was not recorded
CENUND50
species count
number of species 50
data
number
1
real
-9999
Value was not recorded
MEGATL51
species count
number of species 51
data
number
1
real
-9999
Value was not recorded
ANGROS54
species count
number of species 54
data
number
1
real
-9999
Value was not recorded
AMICAL55
species count
number of species 55
data
number
1
real
-9999
Value was not recorded
ANCMIT57
species count
number of species 57
data
number
1
real
-9999
Value was not recorded
CLABAT60
species count
number of species 60
data
number
1
real
-9999
Value was not recorded
MICGUL67
species count
number of species 67
data
number
1
real
-9999
Value was not recorded
ARIFEL69
species count
number of species 69
data
number
1
real
-9999
Value was not recorded
LOPCYP71
species count
number of species 71
data
number
1
real
-9999
Value was not recorded
LUTGRI74
species count
number of species 74
data
number
1
real
-9999
Value was not recorded
FUNGRA75
species count
number of species 75
data
number
1
real
-9999
Value was not recorded
BAGMAR76
species count
number of species 76
data
number
1
real
-9999
Value was not recorded
TILMAR77
species count
number of species 77
data
number
1
real
-9999
Value was not recorded
OREAUR78
species count
number of species 78
data
number
1
real
-9999
Value was not recorded
STRSPP80
species count
number of species 80
data
number
1
real
-9999
Value was not recorded
LAGHOM81
species count
number of species 81
data
number
1
real
-9999
Value was not recorded
CICURO84
species count
number of species 84
data
number
1
real
-9999
Value was not recorded
BELBEL86
species count
number of species 86
data
number
1
real
-9999
Value was not recorded
HEMLET88
species count
number of species 88
data
number
1
real
-9999
Value was not recorded
CARLEU91
species count
number of species 91
data
number
1
real
-9999
Value was not recorded
ARCPRO92
species count
number of species 92
data
number
1
real
-9999
Value was not recorded
SCIOCE94
species count
number of species 94
data
number
1
real
-9999
Value was not recorded
PTEMUL99
species count
number of species 99
data
number
1
real
-9999
Value was not recorded
MACSIA100
species count
number of species 100
data
number
1
real
-9999
Value was not recorded
EUGPLU101
species count
number of species 101
data
number
1
real
-9999
Value was not recorded
KLEMAR102
species count
number of species 102
data
number
1
real
-9999
Value was not recorded
EUCHAR103
species count
number of species 103
data
number
1
real
-9999
Value was not recorded
CYNNEB104
species count
number of species 104
data
number
1
real
-9999
Value was not recorded
CARHIP105
species count
number of species 105
data
number
1
real
-9999
Value was not recorded
GOBROB106
species count
number of species 106
data
number
1
real
-9999
Value was not recorded
MUGCEP107
species count
number of species 107
data
number
1
real
-9999
Value was not recorded
CALSAP109
species count
number of species 109
data
number
1
real
-9999
Value was not recorded
CICSPP110
species count
number of species 110
data
number
1
real
-9999
Value was not recorded
EUCSPP115
species count
number of species 115
data
number
1
real
-9999
Value was not recorded
ELOPSAU117
species count
number of species 117
data
number
1
real
-9999
Value was not recorded
GOBSPP121
species count
number of species 121
data
number
1
real
-9999
Value was not recorded
UNIDEEL200
species count
number of species 200
data
number
1
real
-9999
Value was not recorded
UNIDFISH23
species count
number of species 23
data
number
1
real
-9999
Value was not recorded
CPUE
Total Catch
total number of fish caught per sample
data
number
1
integer
-9999.00
Value was not recorded
Distance
Distance
Total distance shoreline coverd in sample
data
meter
1
integer
-9999.00
Value was not recorded
CPUE100M
catch per unit effort
Catch Per Unit Effort
data
catchPerUnitEffort
1
real
-9999
Value was not recorded
DEPTH_Creek
depth
Depth to Creek bottom
data
meter
0.01
real
-9999.00
Value was not recorded
TEMP
temperature
Temperature
data
celsius
0.1
real
-9999.0
Value was not recorded
DO
dissolved oxygen
Dissolved oxygen
data
milligramsPerLiter
0.01
real
-9999.00
Value was not recorded
Salinity
salinity
Salinity
data
partsPerThousand
0.1
real
-9999.0
Value was not recorded
SH1DSLD
Days since last dry
Number of days since marshes >0
data
number
1
real
9999
Value was not recorded
SH1AVE15D
15 day Avg Marsh depth
15 day Avg Marsh depth
data
centimeter
0.01
real
-9999.00
Value was not recorded
UPDISTANCE
Site distance from marsh
Site distance from marsh
data
kilometer
0.01
real
-9999.00
Value was not recorded
MEANDIST
Site distance from marsh
Site distance from marsh
data
kilometer
0.01
real
-9999.00
Value was not recorded
1018
catch per unit effort
ratio of two quantities as parts per thousand (1:1000)
Short-Term
Type II- These data not necessarily funded only by the NSF.
2014-12-01
This study examines temporal and spatial dynamics in the fish community of the oligohaline to mesohaline reaches of ecotonal creeks along the southwest region of Everglades National Park. In particular, we ask: (a) how does use of these river habitats by fishes change over long and short time scales?, (b) how do these changes relate to variation in abiotic conditions (i.e., salinity and freshwater inflow)?, and (c) how do changes in the fish community relate to anthropogenic activity (both previous drainage and impoundment and restoration efforts )? A key objective of this project is to establish critical pre-restoration baseline conditions for this habitat.
EVR-2013-SCI-0019
These SFWSC research data are being managed by the Florida Coastal Everglades LTER Program.