Contributors | Affiliation | Role |
---|---|---|
Stubbins, Aron | Skidaway Institute of Oceanography (SkIO) | Principal Investigator |
Spencer, Robert | Florida State University (FSU) | Co-Principal Investigator |
Biddle, Mathew | Woods Hole Oceanographic Institution (WHOI BCO-DMO) | BCO-DMO Data Manager |
S-CAN and geochemical data for Groves Creek
In situ instruments deployed at 1 m depth below the surface and as per: Tait, Z. S., M. Thompson, and A. Stubbins (2015) Chemical fouling reduction of a submersible steel spectrophotometer in estuarine environments using a sacrificial zinc anode. Journal of Environmental Quality. doi: 10.2134/jeq2014.11.0484
Samples for laboratory analyses were collected using a refrigerated autosampler (ISCO) which pumped samples from a depth of 1 m below the water surface. Samples were returned to the laboratory and filtered through 0.2 micron Polycap filters within 24 hours of collection.
DOC and TDN using a Shimadzu TOC/TDN analyzer as per automated setup in Stubbins, A., and Dittmar, T. (2012) Low volume quantification of dissolved organic carbon and dissolved nitrogen. Limnology and Oceanography: Methods. doi: 10.4319/lom.2012.10.347.
Lignin via cupric oxide oxidation and GC-MS as per: Spencer, R.G.M., Hernes, P.J., Ruf, R., Baker, A., Dyda, R.Y., Stubbins, A., and Six, J. (2010) Temporal controls on dissolved organic matter and lignin biogeochemistry in a pristine tropical river. Journal of Geophysical Research – Biogeosciences. doi:10.1029/2009JG001180.
Dissolved black carbon by nitric acid oxidation to BPCAs followed by HPLC with spectrophotometric detection as per the non-isotopic method in Wagner, S., Brandes, J., Goranov, A.I., Drake, T. W., Spencer, R. G. W., Stubbins, A. (2017) Online quantification and compound-specific stable isotopic analysis of black carbon in environmental matrices via liquid chromatography-isotope ratio mass spectrometry. Limnology and Oceanography: Methods. doi: 10.1002/lom3.10219.
Nutrients were analyzed using a nutrient analyzer as per: Bittar, T. B., S. A. Berger, L. M. Birsa, T. L. Walters, M. E. Thompson, R. G. M. Spencer, E. L. Mann, A. Stubbins, M. E. Frischer, and J. A. Brandes (2016) Seasonal dynamics of dissolved, particulate and microbial components of a tidal saltmarsh-dominated estuary under contrasting levels of freshwater discharge. Estuarine, Coastal and Shelf Science. doi: 10.1016/j.ecss.2016.08.046.
BCO-DMO Processing Notes:
- combined two data tables into one data table with the same field identifiers.
- added conventional header with dataset name, PI name, version date
- modified parameter names to conform with BCO-DMO naming conventions
- added lat and lon columns
- added date_time column
- added depth column
- removed columns SCAN1,2,3 as the column SCAN_no contains the same information
File |
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light_atten.csv (Comma Separated Values (.csv), 60.90 MB) MD5:66f04f46b5ec28a60d14e25bd43ec764 Primary data file for dataset ID 753816 |
Parameter | Description | Units |
SCAN_no | spectrophotometer number | unitless |
Excel_Time | value that Microsoft Excel recognizes as a date | unitless |
date_time | date and time formatted as a string following YYYY-MM-DD HH:MM | unitless |
ISCO_deployment_no | deployment number | unitless |
nm220 | light attenuation at 220 nanometers | per meter |
nm222_5 | light attenuation at 222.5 nanometers | per meter |
nm225 | light attenuation at 225 nanometers | per meter |
nm227_5 | light attenuation at 227.5 nanometers | per meter |
nm230 | light attenuation at 230 nanometers | per meter |
nm232_5 | light attenuation at 232.5 nanometers | per meter |
nm235 | light attenuation at 235 nanometers | per meter |
nm237_5 | light attenuation at 237.5 nanometers | per meter |
nm240 | light attenuation at 240 nanometers | per meter |
nm242_5 | light attenuation at 242.5 nanometers | per meter |
nm245 | light attenuation at 245 nanometers | per meter |
nm247_5 | light attenuation at 247.5 nanometers | per meter |
nm250 | light attenuation at 250 nanometers | per meter |
nm252_5 | light attenuation at 252.5 nanometers | per meter |
nm255 | light attenuation at 255 nanometers | per meter |
nm257_5 | light attenuation at 257.5 nanometers | per meter |
nm260 | light attenuation at 260 nanometers | per meter |
nm262_5 | light attenuation at 262.5 nanometers | per meter |
nm265 | light attenuation at 265 nanometers | per meter |
nm267_5 | light attenuation at 267.5 nanometers | per meter |
nm270 | light attenuation at 270 nanometers | per meter |
nm272_5 | light attenuation at 272.5 nanometers | per meter |
nm275 | light attenuation at 275 nanometers | per meter |
nm277_5 | light attenuation at 277.5 nanometers | per meter |
nm280 | light attenuation at 280 nanometers | per meter |
nm282_5 | light attenuation at 282.5 nanometers | per meter |
nm285 | light attenuation at 285 nanometers | per meter |
nm287_5 | light attenuation at 287.5 nanometers | per meter |
nm290 | light attenuation at 290 nanometers | per meter |
nm292_5 | light attenuation at 292.5 nanometers | per meter |
nm295 | light attenuation at 295 nanometers | per meter |
nm297_5 | light attenuation at 297.5 nanometers | per meter |
nm300 | light attenuation at 300 nanometers | per meter |
nm302_5 | light attenuation at 302.5 nanometers | per meter |
nm305 | light attenuation at 305 nanometers | per meter |
nm307_5 | light attenuation at 307.5 nanometers | per meter |
nm310 | light attenuation at 310 nanometers | per meter |
nm312_5 | light attenuation at 312.5 nanometers | per meter |
nm315 | light attenuation at 315 nanometers | per meter |
nm317_5 | light attenuation at 317.5 nanometers | per meter |
nm320 | light attenuation at 320 nanometers | per meter |
nm322_5 | light attenuation at 322.5 nanometers | per meter |
nm325 | light attenuation at 325 nanometers | per meter |
nm327_5 | light attenuation at 327.5 nanometers | per meter |
nm330 | light attenuation at 330 nanometers | per meter |
nm332_5 | light attenuation at 332.5 nanometers | per meter |
nm335 | light attenuation at 335 nanometers | per meter |
nm337_5 | light attenuation at 337.5 nanometers | per meter |
nm340 | light attenuation at 340 nanometers | per meter |
nm342_5 | light attenuation at 342.5 nanometers | per meter |
nm345 | light attenuation at 345 nanometers | per meter |
nm347_5 | light attenuation at 347.5 nanometers | per meter |
nm350 | light attenuation at 350 nanometers | per meter |
nm352_5 | light attenuation at 352.5 nanometers | per meter |
nm355 | light attenuation at 355 nanometers | per meter |
nm357_5 | light attenuation at 357.5 nanometers | per meter |
nm360 | light attenuation at 360 nanometers | per meter |
nm362_5 | light attenuation at 362.5 nanometers | per meter |
nm365 | light attenuation at 365 nanometers | per meter |
nm367_5 | light attenuation at 367.5 nanometers | per meter |
nm370 | light attenuation at 370 nanometers | per meter |
nm372_5 | light attenuation at 372.5 nanometers | per meter |
nm375 | light attenuation at 375 nanometers | per meter |
nm377_5 | light attenuation at 377.5 nanometers | per meter |
nm380 | light attenuation at 380 nanometers | per meter |
nm382_5 | light attenuation at 382.5 nanometers | per meter |
nm385 | light attenuation at 385 nanometers | per meter |
nm387_5 | light attenuation at 387.5 nanometers | per meter |
nm390 | light attenuation at 390 nanometers | per meter |
nm392_5 | light attenuation at 392.5 nanometers | per meter |
nm395 | light attenuation at 395 nanometers | per meter |
nm397_5 | light attenuation at 397.5 nanometers | per meter |
nm400 | light attenuation at 400 nanometers | per meter |
nm402_5 | light attenuation at 402.5 nanometers | per meter |
nm405 | light attenuation at 405 nanometers | per meter |
nm407_5 | light attenuation at 407.5 nanometers | per meter |
nm410 | light attenuation at 410 nanometers | per meter |
nm412_5 | light attenuation at 412.5 nanometers | per meter |
nm415 | light attenuation at 415 nanometers | per meter |
nm417_5 | light attenuation at 417.5 nanometers | per meter |
nm420 | light attenuation at 420 nanometers | per meter |
nm422_5 | light attenuation at 422.5 nanometers | per meter |
nm425 | light attenuation at 425 nanometers | per meter |
nm427_5 | light attenuation at 427.5 nanometers | per meter |
nm430 | light attenuation at 430 nanometers | per meter |
nm432_5 | light attenuation at 432.5 nanometers | per meter |
nm435 | light attenuation at 435 nanometers | per meter |
nm437_5 | light attenuation at 437.5 nanometers | per meter |
nm440 | light attenuation at 440 nanometers | per meter |
nm442_5 | light attenuation at 442.5 nanometers | per meter |
nm445 | light attenuation at 445 nanometers | per meter |
nm447_5 | light attenuation at 447.5 nanometers | per meter |
nm450 | light attenuation at 450 nanometers | per meter |
nm452_5 | light attenuation at 452.5 nanometers | per meter |
nm455 | light attenuation at 455 nanometers | per meter |
nm457_5 | light attenuation at 457.5 nanometers | per meter |
nm460 | light attenuation at 460 nanometers | per meter |
nm462_5 | light attenuation at 462.5 nanometers | per meter |
nm465 | light attenuation at 465 nanometers | per meter |
nm467_5 | light attenuation at 467.5 nanometers | per meter |
nm470 | light attenuation at 470 nanometers | per meter |
nm472_5 | light attenuation at 472.5 nanometers | per meter |
nm475 | light attenuation at 475 nanometers | per meter |
nm477_5 | light attenuation at 477.5 nanometers | per meter |
nm480 | light attenuation at 480 nanometers | per meter |
nm482_5 | light attenuation at 482.5 nanometers | per meter |
nm485 | light attenuation at 485 nanometers | per meter |
nm487_5 | light attenuation at 487.5 nanometers | per meter |
nm490 | light attenuation at 490 nanometers | per meter |
nm492_5 | light attenuation at 492.5 nanometers | per meter |
nm495 | light attenuation at 495 nanometers | per meter |
nm497_5 | light attenuation at 497.5 nanometers | per meter |
nm500 | light attenuation at 500 nanometers | per meter |
nm502_5 | light attenuation at 502.5 nanometers | per meter |
nm505 | light attenuation at 505 nanometers | per meter |
nm507_5 | light attenuation at 507.5 nanometers | per meter |
nm510 | light attenuation at 510 nanometers | per meter |
nm512_5 | light attenuation at 512.5 nanometers | per meter |
nm515 | light attenuation at 515 nanometers | per meter |
nm517_5 | light attenuation at 517.5 nanometers | per meter |
nm520 | light attenuation at 520 nanometers | per meter |
nm522_5 | light attenuation at 522.5 nanometers | per meter |
nm525 | light attenuation at 525 nanometers | per meter |
nm527_5 | light attenuation at 527.5 nanometers | per meter |
nm530 | light attenuation at 530 nanometers | per meter |
nm532_5 | light attenuation at 532.5 nanometers | per meter |
nm535 | light attenuation at 535 nanometers | per meter |
nm537_5 | light attenuation at 537.5 nanometers | per meter |
nm540 | light attenuation at 540 nanometers | per meter |
nm542_5 | light attenuation at 542.5 nanometers | per meter |
nm545 | light attenuation at 545 nanometers | per meter |
nm547_5 | light attenuation at 547.5 nanometers | per meter |
nm550 | light attenuation at 550 nanometers | per meter |
nm552_5 | light attenuation at 552.5 nanometers | per meter |
nm555 | light attenuation at 555 nanometers | per meter |
nm557_5 | light attenuation at 557.5 nanometers | per meter |
nm560 | light attenuation at 560 nanometers | per meter |
nm562_5 | light attenuation at 562.5 nanometers | per meter |
nm565 | light attenuation at 565 nanometers | per meter |
nm567_5 | light attenuation at 567.5 nanometers | per meter |
nm570 | light attenuation at 570 nanometers | per meter |
nm572_5 | light attenuation at 572.5 nanometers | per meter |
nm575 | light attenuation at 575 nanometers | per meter |
nm577_5 | light attenuation at 577.5 nanometers | per meter |
nm580 | light attenuation at 580 nanometers | per meter |
nm582_5 | light attenuation at 582.5 nanometers | per meter |
nm585 | light attenuation at 585 nanometers | per meter |
nm587_5 | light attenuation at 587.5 nanometers | per meter |
nm590 | light attenuation at 590 nanometers | per meter |
nm592_5 | light attenuation at 592.5 nanometers | per meter |
nm595 | light attenuation at 595 nanometers | per meter |
nm597_5 | light attenuation at 597.5 nanometers | per meter |
nm600 | light attenuation at 600 nanometers | per meter |
nm602_5 | light attenuation at 602.5 nanometers | per meter |
nm605 | light attenuation at 605 nanometers | per meter |
nm607_5 | light attenuation at 607.5 nanometers | per meter |
nm610 | light attenuation at 610 nanometers | per meter |
nm612_5 | light attenuation at 612.5 nanometers | per meter |
nm615 | light attenuation at 615 nanometers | per meter |
nm617_5 | light attenuation at 617.5 nanometers | per meter |
nm620 | light attenuation at 620 nanometers | per meter |
nm622_5 | light attenuation at 622.5 nanometers | per meter |
nm625 | light attenuation at 625 nanometers | per meter |
nm627_5 | light attenuation at 627.5 nanometers | per meter |
nm630 | light attenuation at 630 nanometers | per meter |
nm632_5 | light attenuation at 632.5 nanometers | per meter |
nm635 | light attenuation at 635 nanometers | per meter |
nm637_5 | light attenuation at 637.5 nanometers | per meter |
nm640 | light attenuation at 640 nanometers | per meter |
nm642_5 | light attenuation at 642.5 nanometers | per meter |
nm645 | light attenuation at 645 nanometers | per meter |
nm647_5 | light attenuation at 647.5 nanometers | per meter |
nm650 | light attenuation at 650 nanometers | per meter |
nm652_5 | light attenuation at 652.5 nanometers | per meter |
nm655 | light attenuation at 655 nanometers | per meter |
nm657_5 | light attenuation at 657.5 nanometers | per meter |
nm660 | light attenuation at 660 nanometers | per meter |
nm662_5 | light attenuation at 662.5 nanometers | per meter |
nm665 | light attenuation at 665 nanometers | per meter |
nm667_5 | light attenuation at 667.5 nanometers | per meter |
nm670 | light attenuation at 670 nanometers | per meter |
nm672_5 | light attenuation at 672.5 nanometers | per meter |
nm675 | light attenuation at 675 nanometers | per meter |
nm677_5 | light attenuation at 677.5 nanometers | per meter |
nm680 | light attenuation at 680 nanometers | per meter |
nm682_5 | light attenuation at 682.5 nanometers | per meter |
nm685 | light attenuation at 685 nanometers | per meter |
nm687_5 | light attenuation at 687.5 nanometers | per meter |
nm690 | light attenuation at 690 nanometers | per meter |
nm692_5 | light attenuation at 692.5 nanometers | per meter |
nm695 | light attenuation at 695 nanometers | per meter |
nm697_5 | light attenuation at 697.5 nanometers | per meter |
nm700 | light attenuation at 700 nanometers | per meter |
nm702_5 | light attenuation at 702.5 nanometers | per meter |
nm705 | light attenuation at 705 nanometers | per meter |
nm707_5 | light attenuation at 707.5 nanometers | per meter |
nm710 | light attenuation at 710 nanometers | per meter |
nm712_5 | light attenuation at 712.5 nanometers | per meter |
nm715 | light attenuation at 715 nanometers | per meter |
nm717_5 | light attenuation at 717.5 nanometers | per meter |
nm720 | light attenuation at 720 nanometers | per meter |
nm722_5 | light attenuation at 722.5 nanometers | per meter |
nm725 | light attenuation at 725 nanometers | per meter |
nm727_5 | light attenuation at 727.5 nanometers | per meter |
nm730 | light attenuation at 730 nanometers | per meter |
DOC_uM | Dissolved Organic Carbon | micro Mole (uM) |
DBC_uM | Dissolved black carbon (DBC) | micro Mole (uM) |
I8_mgper100mgOC_fresh_water | I8 estimate from 8 lignin phenols found in freshwater | units in milligrams lignin per 100 milligrams Organic Carbon |
Lignin_sum8phenol_nM | Dissolved lignin sum8 phenol | nanomole (nM) |
TDN_uM | total dissolved nitrogen (TDN) | micro Mole (uM) |
NO3_NO2_ugNperL | Dissolved nutrients (NO3+NO2) | microgram Nitrogen per Liter (ugN/L) |
NH4_ugNperL | Dissolved nutrients (NH4) | microgram Nitrogen per Liter (ugN/L) |
PO4_ugPperL | Dissolved nutrients (PO4) | microgram Phosphorus per Liter (ugN/L) |
SiO2_mgperL | Dissolved nutrients (SiO2) | miligram per Liter (mg/L) |
WaterLevel_rel_to_MSL | water level relative to Mean Sea Level | meters |
MicroCAT_Salinity | Water salinity | psu |
YSI_Salinity | Water salinity | psu |
Temp_C_MicroCAT | Water temperature | degrees Celsius |
Temp_C_YSI | Water temperature | degrees Celsius |
Flour_CDOM | Colored dissolved organic matter (CDOM fluorescence) | unitless |
Time_Since_Cleaning | Time since cleaning | days |
DO_mgperL_YSI | Dissolved oxygen | miligrams per liter (mg/L) |
B6CA_uM | benzene polycarboxylic acids (B6CA) | microMole (uM) |
B5CA_uM | benzene polycarboxylic acids (B5CA) | microMole (uM) |
B4CA_uM | benzene polycarboxylic acids (B4CA) | microMole (uM) |
BC124_B3CA_uM | benzene polycarboxylic acids (BC124 B3CA) | microMole (uM) |
BC123_B3CA_uM | benzene polycarboxylic acids (BC123 B3CA) | microMole (uM) |
B6CA_B5CA_nM | benzene polycarboxylic acids (B6CA B5CA) | microMole (uM) |
SumS8_ngperL | sum S8 | nanogram per Liter (ng/L) |
SumS6_ngperL | sum S6 | nanogram per Liter (ng/L) |
I6_mgper100mg_OC_for_marine_water | I6 estimate from 6 lignin phenols found in marine water | milligrams lignin per 100 milligrams Organic Carbon |
Manual_Salinity | Salinity | psu |
time_point_type | type of observation (discrete or continuous) | unitless |
lat | latitude north | decimal degrees |
lon | longitude east | decimal degrees |
depth | depth of samples | meters |
Dataset-specific Instrument Name | microcat |
Generic Instrument Name | CTD Sea-Bird MicroCAT 37 |
Dataset-specific Description | In situ temperature and salinity: microcat and YSI sondes |
Generic Instrument Description | The Sea-Bird MicroCAT CTD unit is a high-accuracy conductivity and temperature recorder based on the Sea-Bird SBE 37 MicroCAT series of products. It can be configured with optional pressure sensor, internal batteries, memory, built-in Inductive Modem, integral Pump, and/or SBE-43 Integrated Dissolved Oxygen sensor. Constructed of titanium and other non-corroding materials for long life with minimal maintenance, the MicroCAT is designed for long duration on moorings.
In a typical mooring, a modem module housed in the buoy communicates with underwater instruments and is interfaced to a computer or data logger via serial port. The computer or data logger is programmed to poll each instrument on the mooring for its data, and send the data to a telemetry transmitter (satellite link, cell phone, RF modem, etc.). The MicroCAT saves data in memory for upload after recovery, providing a data backup if real-time telemetry is interrupted. |
Dataset-specific Instrument Name | S-CAN spectrolyzer |
Generic Instrument Name | Spectrometer |
Dataset-specific Description | In situ attenuation: S-CAN spectrolyzer. |
Generic Instrument Description | A spectrometer is an optical instrument used to measure properties of light over a specific portion of the electromagnetic spectrum. |
Dataset-specific Instrument Name | YSI sondes |
Generic Instrument Name | YSI Sonde 6-Series |
Dataset-specific Description | In situ temperature and salinity: microcat and YSI sondes. In situ CDOM fluorescence: YSI sonde |
Generic Instrument Description | YSI 6-Series water quality sondes and sensors are instruments for environmental monitoring and long-term deployments. YSI datasondes accept multiple water quality sensors (i.e., they are multiparameter sondes). Sondes can measure temperature, conductivity, dissolved oxygen, depth, turbidity, and other water quality parameters. The 6-Series includes several models. More from YSI. |
Website | |
Platform | Groves Creek - SkIO |
Start Date | 2013-07-26 |
End Date | 2015-03-11 |
Description | Studies of temporal and compositional changes in exported material in a saltmarsh, both the quantity and quality of dissolved organic matter (DOM) and particulate organic matter (POM) exported from Groves Creek. |
Description from NSF award abstract:
Large fluxes of apparently refractory terrigenous dissolved organic matter (t-DOM) are transported through rivers to the coast each year, yet there are vanishingly low traces of t-DOM in the oceans. The removal of t-DOM is central to the global carbon cycle, yet the mechanisms that drive removal remain poorly understood. In soils, the presence of labile organic compounds is known to enhance the remineralization of recalcitrant compounds, a phenomenon known as the priming effect (PE). The PE is quantitatively important in soil systems, but has received little attention in aquatic systems despite its potential to explain C mineralization patterns at the land-sea interface. This project investigates the magnitude of PE in the coastal ocean and the metabolic and ecological mechanisms that give rise to it. It focuses on the microbial communities of US Atlantic Ocean coastal marshes. In these systems, river-borne t-DOM provides a particularly valuable and tractable model for evaluating the magnitude of the PE. The study utilizes a well-characterized DOM standard collected from a Georgia river as the model t-DOM material in a series of laboratory experiments with natural coastal microbial communities and cultures of heterotrophic marine bacteria of the Roseobacter lineage. Roseobacters are particularly appropriate biological models for this work as they are abundant in southeastern US coastal zones and are known to catabolize lignin and other plant-derived aromatic compounds. Long-term (60 day) incubation experiments will track the PE resulting from addition of labile DOM of differing chemical complexity. Changes in lignin phenols will be the primary measure of the influence of PE on t-DOM degradation, but the research also monitors a broader suite of aromatic compounds represented by optical properties and identified by high-resolution mass spectrometry. Measurements of the microbial response to added labile organic matter, via extracellular enzyme activities, bacterial production, community composition and gene transcript analysis, will reveal the biological mechanisms responsible for the PE. Experiments using Roseobacter strains will allow detailed investigation of the relationship between metabolic pathways, specific bacteria, and organic carbon mineralization in a well-defined experimental system. Data on gene expression, microbial activity, and DOM transformations from the lab experiments will be integrated to elucidate the specific metabolic pathways invoked as part of the PE and guide development of molecular tools to track genetic signatures along a river to coastal ocean transect in the final year of the project.
The role of heterotrophic microorganisms in remineralizing t-DOM at the land-sea interface is a central question in biological oceanography. Components of t-DOM, principally lignin, are refractory in the sense that degradation rates are typically slow relative to other biomolecules, and yet lignin is effectively removed somewhere between land and the open ocean. The project will determine whether priming plays a role in the rapid removal of t-DOM in the coastal ocean, provide evidence for the types of labile organic matter most effective as priming agents, and attemp to discover the metabolic pathways by which the PE is mediated. These studies have the potential to reveal conserved and predictable metabolic responses that may contribute to regulation of the transformation and turnover of naturally occurring semi-labile/refractory DOM in marine environments. As climate change is likely to affect fluxes of both terrigenous carbon and nutrients to the coastal ocean, understanding the magnitude and mechanisms of PE will be necessary to predict the geochemical consequences of these changing fluxes.
This project is related to the project "Tempo and mode of salt marsh exchange" found at https://www.bco-dmo.org/project/564747.
Funding Source | Award |
---|---|
NSF Division of Ocean Sciences (NSF OCE) | |
NSF Division of Ocean Sciences (NSF OCE) |