Contributors | Affiliation | Role |
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Pierson, James J. | University of Maryland Center for Environmental Science (UMCES/HPL) | Principal Investigator |
Decker, Mary Beth | Yale University | Contact |
Houde, Edward | University of Maryland Center for Environmental Science (UMCES/HPL) | Contact |
Roman, Michael R. | University of Maryland Center for Environmental Science (UMCES/HPL) | Contact |
Stoecker, Diane | University of Maryland Center for Environmental Science (UMCES/HPL) | Contact |
Allison, Dicky | Woods Hole Oceanographic Institution (WHOI BCO-DMO) | BCO-DMO Data Manager |
These are the processed CTD data from the DeZoZoo project taken from the mesohaline portion of Chesapeake Bay from 37.5 - 38.5 degrees N and from 76 - 76.5 degrees West.
Data were collected using the shipboard SeaBird 9plus CTD fitted with a variety of sensors. Sensors are listed in the table below:
CTD was lowered to within 2 m of the bottom slowly, with bottom depth determined by CTD mounted altimeter. If samples were collected on a given CTD cast, they were collected as the CTD was raised back to the surface using the attached Rosette fitted with 10L Niskin Bottles.
Sensor | Serial Number |
SBE 9plus pressure | 0445 |
SBE Temperature 1 | 2574 |
SBE Temperature 2 | 2631 |
SBE Conductivity 1 | 2208 |
SBE Conductivity 2 | 2209 |
WetLabs FLNTU | 091 |
SBE 43 Oxygen | 0539 |
C-Star Transmissometer | n/a |
Data were processed according to suggested post-processing routines outlined in the SeaBird Data Processing manual. Headers for the data processing routines are included in the .cnv files of post-processed data. All data were batch processed by cruise using the same routines and averaged in 0.5m bins.
File |
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CTD_DZZ_rs.csv (Comma Separated Values (.csv), 2.95 MB) MD5:7c7520d6cc8d1d4d07ab9d0124db6d26 Primary data file for dataset ID 561249 |
Parameter | Description | Units |
cruise | Cruise Number - first two digits signify year (10 = 2010; 11 = 2011); second two digits signify the sequential number of the cruise in each year | Number |
station | Station Number; in order occupied (1 = South Station; 2 = North Station; 0 = Scanfish Survey) | Number |
campaign | Campaign Number; in order conducted (1 = Anchor; 2 = Trawl; 0 = Scanfish Survey) | Number |
campaign_name | Campaign Name; which identifies both the station and the campaign | Name |
CTD_cast | Consecutive CTD number from each cruise | Number |
lat | North Latitude | Decimal Degrees |
lon | West Longitude | Decimal Degrees |
year | Year data was collected | Year |
month_gmt | Month data was collected | Month |
day_gmt | Day data was collected | Day |
hour_gmt | Hour data was collected | Hour |
minute_gmt | Minute data was collected | Minute |
second_gmt | Second data was collected | Second |
press | Pressure in decibars | db |
temp | Temperature in degrees C from sensor 1 | C |
temp2 | Temperature in degrees C from sensor 2 | C |
cond | Conductivity | S/m |
cond2 | Conductivity | S/m |
O2_volts | Dissolved oxygen voltage | mV |
fluor | Chlorophyll a fluorescence | mg/m3 |
beam_atten | Beam attenuation | 1/m |
beam_trans | Beam transmission | % |
alt | Depth of the altimiter | m |
O2_mg_L | Dissolved oxygen concentration in mg/L | mg/L |
O2_sat | Dissolved oxygen saturation in % | % saturation |
sigma_t | Density in kg/m3 | Kg/m3 |
depth | Depth in saltwater | m |
temp_diff | Temperature difference calculated between different temperature sensors | C |
sal | Salinity from sensor 1 | PSU |
sal2 | Salinity from sensor 2 | PSU |
bin | Number of scans averaged for this bin of data | Number |
flag | Flagged data | n/a |
density_diff | Density difference between the primary and secondary sensors. | Kg/m3 |
ISO_DateTime_UTC | ISO 8601:2004(E) standard for time. Added to the dataset by the DMO. | YYYY-MM-DDTHH:MM:SS.xx |
Dataset-specific Instrument Name | CTD |
Generic Instrument Name | CTD Sea-Bird 911 |
Dataset-specific Description | Standard CTD911+ with fluorometer and oxygen sensors working.
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Generic Instrument Description | The Sea-Bird SBE 911 is a type of CTD instrument package. The SBE 911 includes the SBE 9 Underwater Unit and the SBE 11 Deck Unit (for real-time readout using conductive wire) for deployment from a vessel. The combination of the SBE 9 and SBE 11 is called a SBE 911. The SBE 9 uses Sea-Bird's standard modular temperature and conductivity sensors (SBE 3 and SBE 4). The SBE 9 CTD can be configured with auxiliary sensors to measure other parameters including dissolved oxygen, pH, turbidity, fluorescence, light (PAR), light transmission, etc.). More information from Sea-Bird Electronics. |
Dataset-specific Instrument Name | Fluorometer |
Generic Instrument Name | Fluorometer |
Dataset-specific Description | WET Labs ECO-AFL/FL |
Generic Instrument Description | A fluorometer or fluorimeter is a device used to measure parameters of fluorescence: its intensity and wavelength distribution of emission spectrum after excitation by a certain spectrum of light. The instrument is designed to measure the amount of stimulated electromagnetic radiation produced by pulses of electromagnetic radiation emitted into a water sample or in situ. |
Dataset-specific Instrument Name | Oxygen sensor |
Generic Instrument Name | Sea-Bird SBE 43 Dissolved Oxygen Sensor |
Dataset-specific Description | SBE 43 Oxygen sensor |
Generic Instrument Description | The Sea-Bird SBE 43 dissolved oxygen sensor is a redesign of the Clark polarographic membrane type of dissolved oxygen sensors. more information from Sea-Bird Electronics |
Website | |
Platform | R/V Hugh R. Sharp |
Report | |
Start Date | 2010-05-24 |
End Date | 2010-06-01 |
Description | Cruise in Main Channel of Chesapeake Bay |
Website | |
Platform | R/V Hugh R. Sharp |
Start Date | 2010-08-19 |
End Date | 2010-08-26 |
Description | Cruise in main channel of Chesapeake Bay to collect zooplankton samples. |
Website | |
Platform | R/V Hugh R. Sharp |
Start Date | 2010-09-21 |
End Date | 2010-09-27 |
Description | One of a series of cruises in the main channel of the Chesapeake Bay to collect gelatinous zooplankton. |
Website | |
Platform | R/V Hugh R. Sharp |
Start Date | 2011-05-24 |
End Date | 2011-06-01 |
Description | One of six week-long cruises in the main channel of Chesapeake Bay to collect gelatinous zooplankton. |
Website | |
Platform | R/V Hugh R. Sharp |
Start Date | 2011-07-19 |
End Date | 2011-07-26 |
Description | One of six week-long cruises in the main channel of the Chesapeake Bay to collect gelatinous zooplankton |
Website | |
Platform | R/V Hugh R. Sharp |
Start Date | 2011-09-21 |
End Date | 2011-09-26 |
Description | One of 6 week-long cruises in the main channel of the Chesapeake Bay, collecting gelatinous zooplankton. |
Description from NSF award abstract:
The occurrence of low-oxygen waters, often called "dead zones" in coastal ecosystems throughout the world is increasing. Despite these increases, the pelagic food-web consequences of low-oxygen waters remain poorly understood. Laboratory research has demonstrated that hypoxic water (< 2 mg l-1) can result in mortality, reduced fitness and lower egg production of planktonic copepods, a major link in food webs supporting pelagic fish. Observations in the sea indicate that hypoxic bottom waters usually have depressed abundances of copepods compared to normoxic waters (> 2 mg l-1). The gradient of declining oxygen concentration with respect to depth (oxycline) can be a critical interface in coastal pelagic ecosystems by altering the migratory behavior and depth distribution of copepods and their spatial coherence with potential predators and prey. This project will result in a mechanistic understanding of how behavior and fitness of copepods are affected by hypoxia. The PIs will compare bottom-up and top-down controls on the ecology of copepods in Chesapeake Bay waters experiencing seasonal hypoxia and those that are normoxic.
Specific objectives of this project are to:
1) analyze changes in migratory behavior and fine-scale (meter) distribution of copepods across the oxycline over hourly and diel time scales while simultaneously examining the distribution and abundance of their food (phytoplankton and microzooplankton) and predators (fish, gelatinous zooplankton);
2) estimate effects of hypoxia on the "fitness" of copepods using a suite of measurements (length/weight ratios, feeding, egg production, and egg hatching success) to develop condition indices of copepods captured at different times and depths in hypoxic and normoxic waters; and
3) evaluate effects of hypoxia on copepod mortality by hypoxia-induced, stage-specific copepod mortality in hypoxic bottom waters and by changes in top-down control of copepods from predation by fish and gelatinous zooplankton.
Oxyclines may be a barrier to vertical migration of copepods and thus disruptive to predator avoidance behavior. Faced with increased predation risk from fish and jellyfish, copepods may seek refuge in hypoxic waters for part of the day and/or make short-term vertical excursions between hypoxic and normoxic waters. By regulating vertical migrations, copepods may increase utilization of microzooplankton prey concentrated in the oxycline. Hypoxic waters may elevate consumption of copepods by jellyfish and depress consumption by pelagic fish. This project will evaluate copepod distribution and migration behavior, individual fitness and stage-specific mortality in hypoxic and normoxic waters. It will examine food-web consequences of increased or decreased spatial coherence of copepods and their predators and prey in regions with hypoxic bottom waters and will contribute to fundamental understanding of food-web processes in eutrophic coastal ecosystems.
Project acronym "DeZoZoo" = "Dead Zone Zooplankton"
Funding Source | Award |
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NSF Division of Ocean Sciences (NSF OCE) |