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South Florida
Water, Sustainability, and Climate Project |
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![]() Metadata: Seasonal Electrofishing Data from Rookery Branch and Tarpon Bay, Everglades National Park from November 2004 to Present
Dataset title
Seasonal Electrofishing Data from Rookery Branch and Tarpon Bay, Everglades National Park from November 2004 to Present
Dataset ID
SFWSC_005
Dataset Creator
Metadata Provider
Dataset Abstract
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.
Dataset Keywords
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 Intellectual Rights 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.
Geographic Coverage
Study Extent Description
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
Bounding Coordinates
All Sites
Temporal Coverage
Start Date:
2004-11-01
End Date: 2014-05-05 Maintenance This is a short-term electrofishing dataset and subsequent data will be appended if necessary.
Dataset Contact Methods
Sampling Description
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.
Method Step
Description
Fish were collected via electrofishing methods,
Citation Boucek, Ross E 2013-10-01. No free lunch: displaced marsh consumers regulate a prey subsidy to an estuarine consumer.. Oikos, 122(10): 1453-1464.
Protocol
Protocol Title: Electrofishing
Protocol Creator(s)
Publication Date: 2004-01-01 Abstract 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. Keywords Electrofishing
fish capture Procedural Steps Apply electric current to sampling area
net immobilized fish place fish into a water tank on boat
Instrumentation
21' Aluminum boat fitted with a generator and other electrofishing equipment (see citation 28)
Quality Control
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.
Data Table
Entity Name: SFWSC_005
Entity Description: Seasonal Electrofishing Data from Rookery Branch and Tarpon Bay, Everglades National Park from November 2004 to Present Object Name: SFWSC_005 Data Format
Number of Header Lines: 1
Attribute Orientation: column Field Delimiter: , Number of Records: 1018 Attributes
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This material is based upon work supported by the National Science Foundation under Grant No. EAR-1204762 and the United States Department of Agriculture NIFA Award Number 2012-67003-19862. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Any opinions, findings and conclusions or recommendations expressed in this material are those of the author(s) and do not necessarily reflect the views of the National Science Foundation. |