Contributors | Affiliation | Role |
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Pickering, Rebecca A. | Dauphin Island Sea Lab (DISL) | Principal Investigator |
Krause, Jeffrey W. | Dauphin Island Sea Lab (DISL) | Co-Principal Investigator |
Maiti, Kanchan | Louisiana State University (LSU-DOCS) | Co-Principal Investigator |
Haskins, Christina | Woods Hole Oceanographic Institution (WHOI BCO-DMO) | BCO-DMO Data Manager |
Core Sampling
Briefly, samples were acquired from the study area using an Ocean Instruments MC-900 Multi-corer, which preserved the sediment-water interface during recovery. Overlying bottom water was removed, cores were sectioned into 1cm slices, homogenized, packed under N2 gas and frozen at -20o C for further analysis. On select cores, pore waters were collected prior to core sectioning using Rhizons (0.15 μm pore size; Rhizosphere Research Products) attached to syringes, and inserted into the core (1-cm sediment intervals) through pre-drilled holes. Porewater nutrients were analyzed at the Dauphin Island Sea Lab Analytical Laboratory, via a Skalar San++ Auto Analyzer based on standard Environmental Protection Agency methodologies, including dSi, nitrate plus nitrite (NO3 + NO2), soluble reactive phosphate (PO4) and nitrite (NO2) (μmol L-1).
Operational Definitions
Operational reactive Si pools have previously been defined by Rahman et al. (2016) but for consistency and clarity with previous literature (DeMaster, 1981; Michalopoulos and Aller, 2004; Qin et al., 2012; Wang et al., 2015; Rahman et al., 2016; Krause et al., 2017) it has been restated here. Therefore we use the following nomenclature;
Reactive Silica Pools
Frozen sediment samples were thawed to room temperature (22o C) and triplicate ~50-100 mg subsamples were immediately weighed into 50 mL polyethylene centrifuge tubes. Samples were never dried or ground before/during extractions. Procedural blanks were also prepared in triplicate. Additional subsamples of sediment were dried at 60o C to obtain correction for water content.
Sequential Extractions
Acid Leachable Silica (Si-HCl)
Sediment extractions occurred at room temperature (22o C) using Honeywell Fluka Trace SELECT 0.1 N HCl for 12 hrs, while keeping particles suspended via constant motion. Following centrifugation, the Si-HCl leachate was removed and neutralized. Remaining sediment was rinsed in triplicate with Milli-Q water to remove any residual acid (Michalopoulos and Aller, 2004). As it had previously been demonstrated by Rahman et al. (2016) that the rinses contained minor amounts of Si these rinses were discarded. A weak HCl molarity was purposely chosen to remove metal coatings, authigenic phases, and activate bSi surfaces while not affecting the sequential Si-Alk digestion (Michalopoulos and Aller, 2004).
Mild Alkaline Leachable Si (Si-Alk)
Following the acid pre-leach, the remaining sediment was sequentially digested with 25 ml Fisher Scientific Certified ACS 0.1 M Na2CO3 in an 85o C water bath for a total of 5 hrs. (dry weight SSR ~1-2). Time-point subsamples were taken at 20 min., 1, 2, 3, and 5 hrs. following (DeMaster, 1981). The individual acidified Si-Alk leachates were analyzed for dSi and the intercept from a regression of individual timepoints (DeMaster, 1981) represents the bSiO2 content without LSi interference. After the 5 hrs. aliquot was removed, whole samples were neutralized to stop the digestion. Following centrifugation, the leachate was removed and discarded. Remaining sediment was rinsed in triplicate with Milli-Q water to remove any residual Na2CO3 and again the rinses were discarded.
Harsh NaOH Digestion (Si-NaOH)
The remaining sediment from the Si-Alk treatment was subsequently digested with Honeywell Fluka 4 M NaOH for 2 hrs in a 85o C water bath. After 2 hrs, samples were placed on ice and neutralized to stop the digestion. Following centrifugation, the Si- NaOH leachate was removed, the remaining sediment was rinsed with Milli-Q water to remove any residual leachate and this rinse was added to the Si-NaOH leachate and stored for further analysis (Rahman et al., 2016).
Traditional bSi Digestion (T-bSiO2)
Additionally, a second treatment following the traditional definition of biogenic silica (DeMaster, 1981), with no acid pre-treatment was used. New subsamples of sediment were weighed out. 0.1 M Na2CO3 was added to samples and heated in a 85o C water bath for 20 mins to remove the bSi phase. Following the 20 min timepoint, samples were placed on ice and neutralized to stop the digestion. Following centrifugation, leachate was removed and stored for further use. Similar to the Si-Alk digestions, the process was stopped after 20 mins to ensure the absence of lithogenic material.
A 1 ml aliquot of each resulting liquid (Si-HCl, Si-Alk, Si-NaOH and T-bSi) was analyzed for dissolved SiOH4 concentration (dSi) as described by Brzezinski and Nelson (Brzezinski and Nelson, 1986) using the molybdate-blue method on a Genesys 10S UV-Vis Spectrophotometer. The remaining supernatants were stored following DeMaster (1980) in preparation for future analysis.
Major Metal Compositions and Corrections
Leachate supernatants were evaporated to dryness in Teflon beakers on a hotplate at 100o C and samples were reconstituted in 2% HNO3 (in-house distilled). Major ion concentrations were determined on an Agilent 7700 Series ICP-MS at the Dauphin Island Sea Lab, following calibration using a blank and seven matrix-matched, mixed standards. Internal standards 115In and 4Be (50 μl, 10 ppm) were added to all standards and samples. Samples which could not be resolved from the blank solution were considered operationally undetectable.
Organic Matter
Sediment Particulate organic carbon (POC) and total organic nitrogen (PON) content were analyzed at the Dauphin Island Sea Lab using a Costech elemental combustion system (4010 ECS) following vapor phase acidification to remove carbonates. Briefly, dried sediment samples were placed in a glass desiccator and reacted with reagent-grade 12N HCl vapor for 24 hrs at room temperature. Samples were then dried at 60o C overnight to remove remaining HCl and water content before POC/PON analyses (Yamamuro and Kayanne, 1995).
BCO-DMO Data Manager Processing Notes:
* added a conventional header with dataset name, PI name, version date
* modified parameter names to conform with BCO-DMO naming conventions
* blank values in this dataset are displayed as "nd" for "no data." nd is the default missing data identifier in the BCO-DMO system.
* removed all spaces in headers and replaced with underscores
* removed all units from headers
* converted dates to ISO Format yyyy-mm-dd
* set Types for each data column
File |
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si_sed_pools.csv (Comma Separated Values (.csv), 14.16 KB) MD5:92a0d65db33b64c190005526f4ba110d Primary data file for dataset ID 823190 |
Parameter | Description | Units |
Cruise_Collected | Crusie name and year of collection | unitless |
MultiCore | Multicore identifer for corresponding cruise | unitless |
Station_Number | Station identifier for corresponding cruise | unitless |
Bottom_Depth | Largest veritcal distance below the surface | Meters |
Latitude | Decimal Degrees | Decimal Degrees |
Longitude | Decimal Degrees | Decimal Degrees |
Date_Collected | When was the core collected | yyyy-mm-dd |
Sample_Depth | Subsection used for analysis | centimeters |
Nominal_Depth | Depth used for data plots | centimeters |
Porewater_SiOH_4 | Concentration of dissolved silica acid in porewater collected | micromoles per liter |
Porewater_NO3_NO2 | Concentration of dissolved nitrate-nitrite in porewater collected | micromoles per liter |
Porewater_PO4 | Concentration of dissolved phosphate in porewater collected | micromoles per liter |
Porewater_NO2 | Concentration of dissolved nitrite in porewater collected | micromoles per liter |
Porewater_NH4 | Concentration of dissolved ammonium in porewater collected | micromoles per liter |
Vapor_Phase_Carbonate | % of Carbonates present in the sediment sample via vapor phase acidification | % |
POC | Particular Organic Carbon | % |
POC_2_Stdev | 2 standard deviations of sample variation | dimensionless |
PON | Particular Organic Nitrogen | % |
PON_2_Stdev | 2 standard deviations of sample variation | dimensionless |
Si_HCl | Average Si released (n=3) for each corresponding reactive Si Pool | micromoles per gram dry sediment umol/g |
Si_HCl_2_Stdev | 2 standard deviations for the corresponding reactive Si Pool | dimensionless |
Si_Alk | Average Si released (n=3) for each corresponding reactive Si Pool | micromoles per gram dry sediment umol/g |
Si_Alk_2_Stdev | 2 standard deviations for the corresponding reactive Si Pool | dimensionless |
Si_NaOH | Average Si released (n=3) for each corresponding reactive Si Pool | micromoles per gram dry sediment umol/g |
Si_NaOH_2_Stdev | 2 standard deviations for the corresponding reactive Si Pool | dimensionless |
T_bSiO2 | Average Si released (n=3) for each corresponding reactive Si Pool | micromoles per gram dry sediment umol/g |
T_bSiO2_2_Stdev | 2 standard deviations for the corresponding reactive Si Pool | dimensionless |
Dataset-specific Instrument Name | |
Generic Instrument Name | Costech International Elemental Combustion System (ECS) 4010 |
Generic Instrument Description | The ECS 4010 Nitrogen / Protein Analyzer is an elemental combustion analyser for CHNSO elemental analysis and Nitrogen / Protein determination. The GC oven and separation column have a temperature range of 30-110 degC, with control of +/- 0.1 degC. |
Dataset-specific Instrument Name | Skalar San++ Auto Analyzer |
Generic Instrument Name | Nutrient Autoanalyzer |
Generic Instrument Description | Nutrient Autoanalyzer is a generic term used when specific type, make and model were not specified. In general, a Nutrient Autoanalyzer is an automated flow-thru system for doing nutrient analysis (nitrate, ammonium, orthophosphate, and silicate) on seawater samples. |
Dataset-specific Instrument Name | Genesys 10S UV-Vis Spectrophotometer. |
Generic Instrument Name | Spectrophotometer |
Generic Instrument Description | An instrument used to measure the relative absorption of electromagnetic radiation of different wavelengths in the near infra-red, visible and ultraviolet wavebands by samples. |
Website | |
Platform | R/V Pelican |
Start Date | 2017-05-03 |
End Date | 2017-05-13 |
Description | More information about this cruise can be found in R2R: https://www.rvdata.us/search/cruise/PE17-20 |
NSF Award Abstract:
The Louisiana Shelf system in the northern Gulf of Mexico is fed by the Mississippi River and its many tributaries which contribute large quantities of nutrients from agricultural fertilizer to the region. Input of these nutrients, especially nitrogen, has led to eutrophication. Eutrophication is the process wherein a body of water such as the Louisiana Shelf becomes enriched in dissolved nutrients that increase phytoplankton growth which eventually leads to decreased oxygen levels in bottom waters. This has certainly been observed in this area, and diatoms, a phytoplankton which represents the base of the food chain, have shown variable silicon/nitrogen (Si/N) ratios. Because diatoms create their shells from silicon, their growth is controlled not only by nitrogen inputs but the availability of silicon. Lower Si/N ratios are showing that silicon may be playing an increasingly important role in regulating diatom production in the system. For this reason, a scientist from the University of South Alabama will determine the biogeochemical processes controlling changes in Si/N ratios in the Louisiana Shelf system. One graduate student on their way to a doctorate degree and three undergraduate students will be supported and trained as part of this project. Also, four scholarships for low-income, high school students from Title 1 schools will get to participate in a month-long summer Marine Science course at the Dauphin Island Sea Laboratory and be included in the research project. The study has significant societal benefits given this is an area where $2.4 trillion gross domestic product revenue is tied up in coastal resources. Since diatoms are at the base of the food chain that is the biotic control on said coastal resources, the growth of diatoms in response to eutrophication is important to study.
Eutrophication of the Mississippi River and its tributaries has the potential to alter the biological landscape of the Louisiana Shelf system in the northern Gulf of Mexico by influencing the Si/N ratios below those that are optimal for diatom growth. A scientist from the University of South Alabama believes the observed changes in the Si/N ratio may indicate silicon now plays an important role in regulating diatom production in the system. As such, understanding the biotic and abiotic processes controlling the silicon cycle is crucial because diatoms dominate at the base of the food chain in this highly productive region. The study will focus on following issues: (1) the importance of recycled silicon sources on diatom production; (2) can heavily-silicified diatoms adapt to changing Si/N ratios more effectively than lightly-silicified diatoms; and (3) the role of reverse weathering in sequestering silicon thereby reducing diffusive pore-water transport. To attain these goals, a new analytical approach, the PDMPO method (compound 2-(4-pyridyl)-5-((4-(2-dimethylaminoethylamino-carbamoyl)methoxy)phenyl)oxazole) that quantitatively measures taxa-specific silica production would be used.
Funding Source | Award |
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NSF Division of Ocean Sciences (NSF OCE) |