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Composition and biodegradability of dissolved organic matter leached from eroding coastal soils and permafrost in seawater, from Drew Point, Alaska

General Information
Data Package:
Local Identifier:knb-lter-ble.32.3
Title:Composition and biodegradability of dissolved organic matter leached from eroding coastal soils and permafrost in seawater, from Drew Point, Alaska
Alternate Identifier:DOI PLACE HOLDER
Abstract:

Eroding permafrost coastlines export significant quantities of organic carbon (OC) to the marine environment, similar in magnitude to riverine particulate OC fluxes to the Arctic Ocean. Moreover, erosion rates are predicted to increase due to warming temperatures, declines in sea ice, and increasing waves. While erosion primarily mobilizes organic matter in the particulate form, this material can be leached to dissolved organic matter (DOM). This DOM may be incorporated by microbial communities and fuel marine food webs or decomposed to form greenhouse gases like carbon dioxide and methane. Many studies show that permafrost-derived organic matter can be rapidly decomposed in soils and freshwater, but few studies examine the fate of permafrost organic matter in seawater. To address this knowledge gap, we designed a laboratory experiment to leach coastal soils and permafrost in seawater and examine the composition and biodegradability of leached DOM. Coastal soil/sediment was cored near Drew Point, Alaska in 2019, representing three horizons found within rapidly eroding permafrost bluffs: seasonally thawed active layer soils, Holocene terrestrial soils and/or lacustrine sediments, and late-Pleistocene relict marine sediments. To measure dissolved organic carbon (DOC) leaching yields, we placed soil/sediments in Beaufort Sea seawater for 24 hours before filtering to remove particulates. To measure biodegradable dissolved organic carbon (BDOC), we conducted an aerobic incubation experiment following the methods suggested by Vonk et al. (2015). Briefly, leachates were incubated at approximately room temperature for 26 and 90 days to measure DOC loss due to remineralization and/or incorporation into microbial biomass. Additionally, we used chromophoric dissolved organic matter (CDOM) measurements and ultra-high resolution mass spectrometry (FT-ICR MS) to examine the initial leachate DOM composition.

References:

Vonk, J. E., Tank, S. E., Mann, P. J., Spencer, R. G. M., Treat, C. C., Striegl, R. G., et al. (2015). Biodegradability of dissolved organic carbon in permafrost soils and waterways: a meta-analysis. Biogeosciences Discussions, 12(11), 8353-8393. https://doi.org/10.5194/bgd-12-8353-2015

Short Name:bristol_drew_pt_leaching
Publication Date:2024-04-01
Language:English
For more information:
Visit: https://ble.lternet.edu
Visit: DOI PLACE HOLDER

People and Organizations
Contact:Information Manager (Beaufort Lagoon Ecosystems LTER) [  email ]
Creator:Bristol, Emily M (United States Geological Survey)
Creator:Behnke, Megan I (Dept. of Natural Sciences, U. of Alaska Southeast)
Creator:Spencer, Robert G. M. (Florida State University)
Creator:McKenna, Amy (Florida State University)
Creator:Jones, Benjamin M (The University of Alaska at Fairbanks)
Creator:Bull, Diana L (Sandia National Laboratories)
Creator:McClelland, James W (Marine Biological Laboratory)
Associate:Mohandas, Induja (The University of Texas at Austin, information manager)
Associate:Whiteaker, Timothy L (The University of Texas at Austin, information manager)

Data Entities
Data Table Name:
Dissolved organic carbon leaching and biodegradability measurements
Description:
Results from soil/permafrost leaching and biodegradable dissolved organic carbon incubation experiment. Includes soil organic carbon content, DOC leaching yields, initial leachate DOC concentrations, and DOC loss measurements.
Data Table Name:
Composition of leachate dissolved organic matter
Description:
Measurements of the composition of dissolved organic matter leached from soils/permafrost in seawater. Includes chromophoric dissolved organic matter (CDOM) indicies and summerized ultra-high resolution mass spectrometry (FT-ICR MS) data.
Detailed Metadata

Data Entities


Data Table

Data:https://pasta-s.lternet.edu/package/data/eml/knb-lter-ble/32/3/1d61dc10b5f48208a2811b0c60b15377
Name:Dissolved organic carbon leaching and biodegradability measurements
Description:Results from soil/permafrost leaching and biodegradable dissolved organic carbon incubation experiment. Includes soil organic carbon content, DOC leaching yields, initial leachate DOC concentrations, and DOC loss measurements.
Number of Records:12
Number of Columns:14

Table Structure
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Table Column Descriptions
 Leachate IDgeomorphicTerrainUnitlatitudelongitudehorizondepth_cmSOC_percentleachateDOC_t0_mg_LleachingYield_mg_DOC_g_SOCleachingYield_mg_DOC_g_dwDOCloss_t26_mg_LDOCloss_t90_mg_LbiodegradableDOC_t26_percentbiodegradableDOC_t90_percent
Column Name:leachateID  
geomorphicTerrainUnit  
latitude  
longitude  
horizon  
depth_cm  
SOC_percent  
leachateDOC_t0_mg_L  
leachingYield_mg_DOC_g_SOC  
leachingYield_mg_DOC_g_dw  
DOCloss_t26_mg_L  
DOCloss_t90_mg_L  
biodegradableDOC_t26_percent  
biodegradableDOC_t90_percent  
Definition:Unique identifier for soil/permafrost leachateClassification of landscape surface geomorphologyLatitude in decimal degrees (WGS84)Longitude in decimal degrees (WGS84)Classification of the soil/permafrost horizon sampledDepth of soil/permafrost sample from the tundra surfaceSoil/permafrost organic carbon contentLeachate dissolved organic carbon at t0DOC leaching yield from soils/sediments in seawater for 24 hours, normalized by soil/sediment organic carbon, reported in mg DOC per gram of SOCDOC leaching yield from soils/sediments in seawater for 24 hours, normalized by soil/sediment dry weight, reported in mg DOC per gram of soil/permafrost dry weightAbsolute DOC loss throughout a 26 day dark aerobic incubationAbsolute DOC loss throughout a 90 day dark aerobic incubationBiodegradable DOC, measured as the percent loss of leached DOC after a 26 day dark aerobic incubationBiodegradable DOC, measured as the percent loss of leached DOC after a 90 day dark aerobic incubation
External Measurement Definition, Link: containsMeasurementsOfType organic carbon percentage in soil containsMeasurementsOfType dissolved organic carbon containsMeasurementsOfType dissolved organic carbon containsMeasurementsOfType dissolved organic carbon containsMeasurementsOfType biodegradable dissolved organic carbon containsMeasurementsOfType biodegradable dissolved organic carbon
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Definitionany text
Allowed Values and Definitions
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Code Definition
Codeprimary_surface
DefinitionTerrain that has not been reworked by thaw-lake cycles.
Source
Code Definition
Codeyoung_dtlb
DefinitionA young drained thermokarst lake basin where the last drainage occurred in the last 500 years BP.
Source
Unitdegree
Typereal
Min-90 
Max90 
Unitdegree
Typereal
Min-180 
Max180 
Allowed Values and Definitions
Enumerated Domain 
Code Definition
CodeTerrestrial Permafrost
DefinitionPermafrost composed of Holocene age terrestrial soils and/or lacustrine sediments
Source
Code Definition
CodeActive Layer
DefinitionSeasonally thawed, active layer soils
Source
Code Definition
CodeMarine Permafrost
DefinitionPermafrost composed of Pleistocene age relict marine sediment. These relict sediements are are present in eroding bluffs above and below modern sea level.
Source
Unitcentimeter
Typereal
Unitpercent
Typereal
UnitmilligramsPerLiter
Typereal
UnitmilligramPerGram
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UnitmilligramPerGram
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UnitmilligramsPerLiter
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Data Table

Data:https://pasta-s.lternet.edu/package/data/eml/knb-lter-ble/32/3/d03a36eaac91a9b04af81372a5bb55bc
Name:Composition of leachate dissolved organic matter
Description:Measurements of the composition of dissolved organic matter leached from soils/permafrost in seawater. Includes chromophoric dissolved organic matter (CDOM) indicies and summerized ultra-high resolution mass spectrometry (FT-ICR MS) data.
Number of Records:12
Number of Columns:23

Table Structure
Object Name:BLE_LTER_leachate_DOM_composition.csv
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Table Column Descriptions
 Leachate IDgeomorphicTerrainUnitlatitudelongitudehorizondepth_cmspectralSlope275_295_nm-1spectralSlopeRatioSUVA254_L_mg-DOC-1_m-1number_formulaemassNOSCAImodsugar_like_percentRApeptide_like_percentRAaliphatics_percentRAhighlyUnsaturatedAndPhenolics_percentRApolyphenolics_percentRAcondensedAromatics_percentRACHO_percentRACHON_percentRACHONS_percentRACHOS_percentRA
Column Name:leachateID  
geomorphicTerrainUnit  
latitude  
longitude  
horizon  
depth_cm  
spectralSlope275_295_nm-1  
spectralSlopeRatio  
SUVA254_L_mg-DOC-1_m-1  
number_formulae  
mass  
NOSC  
AImod  
sugar_like_percentRA  
peptide_like_percentRA  
aliphatics_percentRA  
highlyUnsaturatedAndPhenolics_percentRA  
polyphenolics_percentRA  
condensedAromatics_percentRA  
CHO_percentRA  
CHON_percentRA  
CHONS_percentRA  
CHOS_percentRA  
Definition:Unique id for soil/permafrost leachateClassification of landscape surface geomorphologyLatitude in decimal degrees (WGS84)Longitude in decimal degrees (WGS84)Classification of the soil/permafrost horizon sampledDepth of soil/permafrost sample from the tundra surfaceSlope of 275-295 nm region of log-transformed CDOM absorption spectraRatio of 275-295 nm to 350-400 nm spectral slopes from log-transformed CDOM absorption spectraSpecific ultraviolet absorption at 254 nmNumber of unique molecular formulae identified with FT-ICR MSRelative intensity weighted average molecular weightRelative intensity weighted average nominal oxidation state of carbonModified aromaticity indexPercent relative abundance of formulae classified as sugar likePercent relative abundance of formulae classified as peptide likePercent relative abundance of formulae classified as aliphaticPercent relative abundance of formulae classified as highly unsaturated and phenolicPercent relative abundance of formulae classified as polyphenolicPercent relative abundance of formulae classified as condensed aromaticPercent relative abundance of formulae that did not contain nitrogen or sulfurPercent relative abundance of formulae that contained nitrogen but no sulfurPercent relative abundance of formulae that contained nitrogen and sulfurPercent relative abundance of formulae that contained sulfur but not nitrogen
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decimal  
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decimal  
decimal  
decimal  
decimal  
decimal  
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Measurement Values Domain:
Definitionany text
Allowed Values and Definitions
Enumerated Domain 
Code Definition
Codeyoung_dtlb
DefinitionA young drained thermokarst lake basin where the last drainage occurred in the last 500 years BP.
Source
Code Definition
Codeprimary_surface
DefinitionTerrain that has not been reworked by thaw-lake cycles.
Source
Unitdegree
Typereal
Min-90 
Max90 
Unitdegree
Typereal
Min-180 
Max180 
Allowed Values and Definitions
Enumerated Domain 
Code Definition
CodeTerrestrial Permafrost
DefinitionPermafrost composed of Holocene age terrestrial soils and/or lacustrine sediments
Source
Code Definition
CodeMarine Permafrost
DefinitionPermafrost composed of Pleistocene age relict marine sediment. These relict sediements are are present in eroding bluffs above and below modern sea level.
Source
Code Definition
CodeActive Layer
DefinitionSeasonally thawed, active layer soils
Source
Unitcentimeter
Typereal
UnitinverseNanometer
Typereal
Unitdimensionless
Typereal
UnitliterPerMilligramPerMeter
Typereal
Unitnumber
Typereal
Unitdalton
Typereal
Unitdimensionless
Typereal
Unitdimensionless
Typereal
Unitpercent
Typereal
Unitpercent
Typereal
Unitpercent
Typereal
Unitpercent
Typereal
Unitpercent
Typereal
Unitpercent
Typereal
Unitpercent
Typereal
Unitpercent
Typereal
Unitpercent
Typereal
Unitpercent
Typereal
Missing Value Code:                                              
Accuracy Report:                                              
Accuracy Assessment:                                              
Coverage:                                              
Methods:                                              

Data Package Usage Rights

This data package is released to the public domain under Creative Commons CC0 1.0 “No Rights Reserved” (see: https://creativecommons.org/publicdomain/zero/1.0/). It may be distributed, remixed, and built upon. You may do so in any reasonable manner, but not in any way that suggests the licensor endorses you or your use. It is considered professional etiquette to provide attribution of the original work if this data package is shared or utilized in whole or by individual components. A generic citation is provided for this data package on the website of the repository where these data were obtained in the summary metadata page.

Communication (and collaboration) with the creators of this data package is recommended to prevent duplicate research or publication. The consumer of these data ("Data User" herein) is urged to contact the authors of these data if any questions about methodology or results occur. The Data User should realize that these data may be actively used by others for ongoing research and that coordination may be necessary to prevent duplication or inappropriate use. Where appropriate, the Data User is encouraged to consider collaboration or co-authorship with the authors. The Data User should realize that misinterpretation may occur if data are used outside of the context of the original study. The Data User should be aware that periodic updates of this data package may be available from the website and it is the responsibility of the Data User to check for new versions of the data.

While substantial efforts are made to ensure the accuracy of data and associated documentation, complete accuracy cannot be guaranteed. This data package (with its components) is made available “as is” and with no warranty of accuracy or fitness for use. The creators of this data package and the repository where these data were obtained shall not be liable for any damages resulting from misinterpretation, use or misuse of the data package or its components. Thank you.

External Annotations

With link(s) out to external vocabularies
Dataset isAbout leachate
Dataset isAbout permafrost

Keywords

By Thesaurus:
LTER Core Research Areasmovement of organic matter
LTER Controlled Vocabulary v1decomposition, dissolved organic carbon, erosion, organic matter, permafrost
Geographic Names Information SystemDrew Point
BLE LTER Controlled VocabularyFourier transform ion cyclotron resonance, FT-ICR MS, mass spectrometry, soil leaching

Methods and Protocols

These methods, instrumentation and/or protocols apply to all data in this dataset:

Methods and protocols used in the collection of this data package
Description:

Sample collection

Active layer and permafrost samples were collected from exposed bluffs near Drew Point during August 10-14, 2019. Three active layer (i.e. seasonally thawed) samples, three shallow permafrost samples, and three deeper permafrost samples were sampled from a young (approximately 500 yr BP) drained thermokarst lake basin (Hinkel et al., 2003; Jones et al., 2012). An additional three active layer samples were sampled from primary material that has never been reworked by thaw-lake cycles. Previous work has shown that the upper, organic rich permafrost horizon at Drew Point consists of Holocene terrestrial soils and/or lacustrine sediments, and that the lower mineral permafrost horizon consists of late-Pleistocene relict marine sediment (Bristol et al., 2021).

Samples from the drained lake basin were collected by scraping thawed material from exposed bluff before coring horizontally with a 7.5 cm diameter SIPRE core auger. Due to tall (~6m), steep bluffs at the primary surface site, active layer samples were collected by drilling vertically from the tundra surface to a depth of approximately 35 cm; these cores were subsampled to capture a similar depth range as horizontal cores. The SIPRE core barrel was wiped clean in between samples, and the average depth of the sample was measured from the tundra surface. Core sections were stored in clean Ziplock bags inside coolers packed with ice or frozen permafrost and transported back to the Barrow Arctic Research Center in Utqiagvik, Alaska by helicopter or float plane. Samples were stored in at -20C in a freezer at the Barrow Arctic Research Center until transported frozen back to the University of Texas Marine Science Institute. Seawater used for the experiment was collected from Beaufort Sea surface waters near Kaktovik, AK during August 2018, run through pre-combusted Whatman GF/F (0.7 um) filters, transported frozen to the University of Texas Marine Science Institute, and stored at -20C. The seawater had a salinity of 31.

Dissolved Organic Carbon Leaching

Active layer and permafrost samples were thawed at 4C and gently homogenized. Then, subsamples were taken to measure soil/permafrost organic carbon (OC) content (see "Bulk Geochemical Analyses") and water content. After subsampling, the homogenized soil/sediments were refrozen so that soil/permafrost OC could be quantified before leaching. Slurries were formed by combining thawed soil/permafrost samples with 700 mL GF/F filtered seawater in pre-combusted beakers. We normalized the soil/permafrost OC added to each slurry with a target concentration of 5 g OC L-1. This was equivalent to ~75-550 g wet soil/sediment L-1, depending on OC and water content, and resulted in high DOC concentrations. To act as a control, one beaker contained only seawater. The slurries and seawater control were covered and stored in the dark, gently stirring three times throughout the leaching period. After 24 hours, the slurries and seawater control were decanted and vacuum filtered using pre-combusted GF/F filters.

Biodegradable Dissolved Organic Carbon

To facilitate comparison with other studies, we generally followed the standardized biodegradable dissolved organic carbon (BDOC) protocol suggested by Vonk et al. (2015). This lability assay measures DOC loss throughout an incubation, often 28 days at room temperature, in the dark to prevent photochemical reactions or primary production. Initial samples are 0.7 um filtered before the incubation, removing particulate matter but allowing some microbial biomass to pass through. At the end of the incubation period, samples are re-filtered (0.7 um) to remove any bacterial aggregates that may have formed. Therefore, the DOC loss represents DOC that was respired and/or incorporated into microbial biomass.

Immediately after filtering the slurries, each leachate and the seawater control were subsampled for initial chemical analyses (i.e., DOC concentrations, CDOM, FT-ICR MS). Acid washed, pre-leached polycarbonate bottles were used throughout the experiment. Each leachate and the seawater control were incubated in triplicate in the dark on a shaker table in an environmental chamber and sampled at 26 and 90 days. The incubation temperature averaged 19C. Bottles were sealed to prevent evaporation but had a 1:1 solution to headspace ratio and were uncapped and aerated for 10 minutes weekly. After 26 and 90 days, triplicate sets of bottles were re-filtered to remove large microbial biomass aggregates using pre-combused GF/F filters and analyzed for DOC concentrations.

Bulk Geochemical Analyses

Subsamples for soil/sediment TOC (%) analysis were acidified with 10% ultrapure HCl in silver capsules before carbon mass was analyzed with a Thermo Fisher EA-Isolink-CNSOH elemental analyzer. Concentrations of DOC were measured with a Shimadzu TOC-V CSH analyzer. Samples were acidified to a pH of 2 with concentrated HCl (ACS reagent grade; JT Baker) immediately after filtering and DOC concentrations were analyzed within 24 hours.

Subsamples for CDOM were stored at 4C and measured within 24 hours using an Ocean Optics UV-visible light absorbance spectrophotometer. Ultrapure water blanks were run approximately every 5 samples and used to correct sample spectra. Parameters S275-295 (log-transformed spectral slope between 275 and 295 nm) and SR (275-295 nm slope:350-400 nm slope) were calculated from CDOM spectra according to Helms et al. (2008). The specific ultra-violet absorbance at 254 nm (SUVA254; decadic absorbance at 254 nm normalized by DOC concentration in mg L-1) was calculated according to Weishaar et al. (2003). All bulk chemical analyses were completed at the University of Texas Marine Science Institute.

Ultra-High Resolution Mass Spectrometry

Leachate DOM samples for FT-ICR MS analyses (t0 only) were solid phase extracted onto reverse phase BondElut PPL cartridges (100 mg; Agilent) following an established protocol (Dittmar et al., 2008). Briefly, leachate subsamples were acidified to a pH of 2 with HCl, passed through pre-conditioned PPL cartridges, rinsed with acidified water, and eluted with 1 mL methanol for a target concentration of 40 ug C mL-1. ACS reagent grade HCl (JT Baker) and LC/MS grade methanol and water (Fisher Chemical) were used throughout.

Extracts were stored in methanol at -20 degrees C until analysis on a custom-built hybrid linear ion trap 21 T FT-ICR MS at the National High Magnetic Field Laboratory in Tallahassee, Florida (Hendrickson et al., 2015; Smith et al., 2018) using negative electrospray ionization. For each spectrum, 100 time domain acquisitions were co-added. Mass spectra were phase-corrected (Xian et al., 2010) and molecular formulae assigned to peaks that had >6σ root-mean-square baseline noise (Behnke et al., 2021; O'Donnell et al., 2016) with PetroOrg © TM software (Corilo, 2015). Formulae were assigned using elemental constraints of C1-45H1-92O0-35N0-4S0-2 and with a mass accuracy less than or equal to 300 ppb (Kellerman et al., 2018). The modified aromaticity index (AImod) was calculated from the molecular formulae to measure the degree of aromaticity (Koch & Dittmar, 2006, 2016). Elemental ratios and AImod were used to assign the following compound classes to the molecular formulae: polyphenolics (0.5 < AImod > 0.66); condensed aromatics (AImod > 0.66); highly unsaturated and phenolics (HUPs; AImod<=0.5, H/C < 1.5, O/C <= 0.9); aliphatic (1.5 <= H/C <= 2.0, O/C <= 0.9 and N = 0); sugar-like (O/C > 0.9); and peptide-like (1.5 <= H/C <=2.0, and N > 0) (Behnke et al., 2021). Each assigned molecular formula may contain multiple isomers, and compound structure cannot be assessed from FT-ICR MS data. The relative abundance of each formula was calculated by normalizing each peak magnitude to the sum of all peak magnitudes assigned in each sample. The relative contributions (expressed as percentages) of each compound class and elemental composition grouping (e.g., CHO, CHON) were then calculated as the sum of all the relative abundances of all the peaks in each compound class divided by the sum of all the assigned formulae abundances in each sample.

Data Analyses

Results from samples incubated in triplicate were averaged. DOC leaching yields were calculated using the t0 leachate concentrations normalized by both soil/permafrost dry weight and OC content accounting for DOC in the seawater (1.2 mg-C L-1). Here, we report the absolute loss of DOC as well as the percent loss of DOC (i.e., biodegradable DOC; BDOC) at each timepoint. There was no detectible change in seawater control DOC concentrations throughout the incubation experiment indicating there was no biodegradable DOC in the seawater. Therefore, BDOC reported here is the percent loss ofleached DOC where the leached DOC concentration is equivalent to the measured leachate DOC concentration minus the measured seawater control DOC concertation.

References

Behnke, M. I., McClelland, J. W., Tank, S. E., Kellerman, A. M., Holmes, R. M., Haghipour, N., et al. (2021). Pan-Arctic Riverine Dissolved Organic Matter: Synchronous Molecular Stability, Shifting Sources and Subsidies. Global Biogeochemical Cycles, 35(4). https://doi.org/10.1029/2020GB006871

Bristol, E. M., Connolly, C. T., Lorenson, T. D., Richmond, B. M., Ilgen, A. G., Choens, R. C., et al. (2021). Geochemistry of Coastal Permafrost and Erosion-Driven Organic Matter Fluxes to the Beaufort Sea Near Drew Point, Alaska. Frontiers in Earth Science, 8, 598933. https://doi.org/10.3389/feart.2020.598933

Corilo, Y. E. (2015). PetroOrg Software. Florida State University, Tallahassee, FL: Omics LLC.

Helms, J. R., Stubbins, A., Ritchie, J. D., Minor, E. C., Kieber, D. J., & Mopper, K. (2008). Absorption spectral slopes and slope ratios as indicators of molecular weight, source, and photobleaching of chromophoric dissolved organic matter. Limnology and Oceanography, 53(3), 955-969. https://doi.org/10.4319/lo.2008.53.3.0955

Hendrickson, C. L., Quinn, J. P., Kaiser, N. K., Smith, D. F., Blakney, G. T., Chen, T., et al. (2015). 21 Tesla Fourier Transform Ion Cyclotron Resonance Mass Spectrometer: A National Resource for Ultrahigh Resolution Mass Analysis. Journal of the American Society for Mass Spectrometry, 26(9), 1626-1632. https://doi.org/10.1007/s13361-015-1182-2

Hinkel, K. M., Eisner, W. R., Bockheim, J. G., Nelson, F. E., Peterson, K. M., & Dai, X. (2003). Spatial Extent, Age, and Carbon Stocks in Drained Thaw Lake Basins on the Barrow Peninsula, Alaska. Arctic, Antarctic, and Alpine Research, 35(3), 291-300. https://doi.org/10.1657/1523-0430(2003)035[0291:SEAACS]2.0.CO;2

Jones, M. C., Grosse, G., Jones, B. M., & Walter Anthony, K. (2012). Peat accumulation in drained thermokarst lake basins in continuous, ice-rich permafrost, northern Seward Peninsula, Alaska. Journal of Geophysical Research: Biogeosciences, 117(G2). https://doi.org/10.1029/2011JG001766

Kellerman, A. M., Guillemette, F., Podgorski, D. C., Aiken, G. R., Butler, K. D., & Spencer, R. G. M. (2018). Unifying Concepts Linking Dissolved Organic Matter Composition to Persistence in Aquatic Ecosystems. Environmental Science & Technology, 52(5), 2538-2548. https://doi.org/10.1021/acs.est.7b05513

Koch, B. P., & Dittmar, T. (2006). From mass to structure: an aromaticity index for high-resolution mass data of natural organic matter. Rapid Communications in Mass Spectrometry, 20(5), 926-932. https://doi.org/10.1002/rcm.2386

Koch, B. P., & Dittmar, T. (2016). From mass to structure: an aromaticity index for high-resolution mass data of natural organic matter. Rapid Communications in Mass Spectrometry, 30(1), 250-250. https://doi.org/10.1002/rcm.7433

O'Donnell, J. A., Aiken, G. R., Butler, K. D., Guillemette, F., Podgorski, D. C., & Spencer, R. G. M. (2016). DOM composition and transformation in boreal forest soils: The effects of temperature and organic-horizon decomposition state. Journal of Geophysical Research: Biogeosciences, 121(10), 2727-2744. https://doi.org/10.1002/2016JG003431

Smith, D. F., Podgorski, D. C., Rodgers, R. P., Blakney, G. T., & Hendrickson, C. L. (2018). 21 Tesla FT-ICR Mass Spectrometer for Ultrahigh-Resolution Analysis of Complex Organic Mixtures. Analytical Chemistry, 90(3), 2041-2047. https://doi.org/10.1021/acs.analchem.7b04159

Vonk, J. E., Tank, S. E., Mann, P. J., Spencer, R. G. M., Treat, C. C., Striegl, R. G., et al. (2015). Biodegradability of dissolved organic carbon in permafrost soils and waterways: a meta-analysis. Biogeosciences Discussions, 12(11), 8353-8393. https://doi.org/10.5194/bgd-12-8353-2015

Weishaar, J. L., Aiken, G. R., Bergamaschi, B. A., Fram, M. S., Fujii, R., & Mopper, K. (2003). Evaluation of Specific Ultraviolet Absorbance as an Indicator of the Chemical Composition and Reactivity of Dissolved Organic Carbon. Environmental Science & Technology, 37(20), 4702-4708. https://doi.org/10.1021/es030360x

Xian, F., Hendrickson, C. L., Blakney, G. T., Beu, S. C., & Marshall, A. G. (2010). Automated Broadband Phase Correction of Fourier Transform Ion Cyclotron Resonance Mass Spectra. Analytical Chemistry, 82(21), 8807-8812. https://doi.org/10.1021/ac101091w

People and Organizations

Publishers:
Organization:Environmental Data Initiative
Email Address:
info@edirepository.org
Web Address:
https://edirepository.org
Id:https://ror.org/0330j0z60
Creators:
Individual: Emily M Bristol
Organization:United States Geological Survey
Address:
Pacific Coastal and Marine Science Center 2885 Mission St,
Santa Cruz, CA 95060 USA
Email Address:
ebristol@usgs.gov
Id:https://orcid.org/0000-0002-6059-3771
Individual: Megan I Behnke
Organization:Dept. of Natural Sciences, U. of Alaska Southeast
Address:
Juneau, AK USA
Id:https://orcid.org/0000-0002-9654-9078
Individual: Robert G. M. Spencer
Organization:Florida State University
Address:
Dept. of Earth, Ocean, and Atmospheric Science,
Talahassee, FL USA
Id:https://orcid.org/0000-0003-0777-0748
Individual: Amy McKenna
Organization:Florida State University
Address:
National High Magnetic Field Laboratory,
Talahassee, FL USA
Id:https://orcid.org/0000-0001-7213-521X
Individual: Benjamin M Jones
Organization:The University of Alaska at Fairbanks
Address:
Institute of Northern Engineering,
Fairbanks, AK USA
Email Address:
bmjones3@alaska.edu
Id:https://orcid.org/0000-0002-1517-4711
Individual: Diana L Bull
Organization:Sandia National Laboratories
Address:
Albuquerque, NM USA
Email Address:
dlbull@sandia.gov
Id:https://orcid.org/0000-0001-7234-9285
Individual: James W McClelland
Organization:Marine Biological Laboratory
Address:
Marine Biological Laboratory 7 MBL Street,
Woods Hole, MA 02543 USA
Phone:
508-289-7162
Email Address:
jmcclelland@mbl.edu
Web Address:
https://www.mbl.edu/research/faculty-and-whitman-scientists/James%20McClelland
Id:https://orcid.org/0000-0001-9619-8194
Contacts:
Organization:Beaufort Lagoon Ecosystems LTER
Position:Information Manager
Address:
MC R8000 The University of Texas at Austin,
Austin, TX 78712 USA
Email Address:
BLE-IM@utexas.edu
Web Address:
https://ble.lternet.edu/
Id:https://ror.org/055a54548
Associated Parties:
Individual: Induja Mohandas
Organization:The University of Texas at Austin
Address:
Austin, TX 78758 USA
Email Address:
induja.mohandas@austin.utexas.edu
Id:https://orcid.org/0009-0002-8475-2295
Role:information manager
Individual: Timothy L Whiteaker
Organization:The University of Texas at Austin
Address:
Austin, TX 78758 USA
Email Address:
whiteaker@utexas.edu
Id:https://orcid.org/0000-0002-1940-4158
Role:information manager
Metadata Providers:
Organization:Beaufort Lagoon Ecosystems LTER
Address:
750 Channel View Dr.,
Port Aransas, TX 78373 USA
Email Address:
BLE-IM@utexas.edu
Web Address:
https://ble.lternet.edu/
Id:https://ror.org/055a54548

Temporal, Geographic and Taxonomic Coverage

Temporal, Geographic and/or Taxonomic information that applies to all data in this dataset:
Geographic Region:
Description:Bounding box of sampling area, knb-lter-ble.32: Drew Point, North Slope, Alaska, USA.
Bounding Coordinates:
Northern:  70.886360Southern:  70.879880
Western:  -153.898520Eastern:  -153.699830

Project

Parent Project Information:

Title:Arctic Coastal Erosion: Modeling and Experimentation, Sandia National Laboratories
Personnel:
Organization:Sandia National Laboratories
Address:
P.O. Box 5800,
Albuquerque, NM 78373 USA
Web Address:
https://sandia.gov/
Id:https://ror.org/01apwpt12
Role:Lead organization
Abstract:

Arctic coastal erosion rates are accelerating due to increases in temperature, declines in sea ice extent, and the increasing length of the open-water season. Increasing erosion puts critical infrastructure and native communities at risk. Additionally, erosion mobilizes large quantities of organic-rich permafrost to the ocean where it may be decomposed, producing greenhouse gases. While Arctic coastlines compromise one-third of the global coastline, current models for estimating erosion are unable to adequately explain episodic, storm-driven events. This Arctic coastal erosion modeling project mechanistically coupled oceanographic and atmospheric boundary conditions with a terrestrial permafrost model to capture the thermo, chemical, and mechanical dynamics of erosion.

To aid development of the terrestrial model component and to estimate land-to-ocean fluxes of geochemical constituents, we completed extensive analyses of permafrost cored near Drew Point, Alaska, including geochemical and material properties of these permafrost core samples.

See the project report at https://www.osti.gov/biblio/1670531.

Funding:

This work was supported by the Laboratory Directed Research and Development program at Sandia National Laboratories, a multimission laboratory managed and operated by National Technology and Engineering Solutions of Sandia LLC, a wholly owned subsidiary of Honeywell International Inc. for the U.S. Department of Energy's National Nuclear Security Administration under contract DE-NA0003525. Graduate student participation at the University of Texas at Austin (E.B. and C.C.) was supported by an Academic Alliance Partnership plus-up on the LDRD project. J.C. and S.B. were supported by the EMERGE Biology Integration Institute of the National Science Foundation (NSF award 2022070). Additionally, the National Science Foundation provided support for B.J. (OPP-1806213, OISE-1927553) and M.K. (OPP-1820883). USGS personnel were supported by the USGS Coastal Hazards Program and the Alaska Coastal Processes and Hazards Project team. The Beaufort Lagoon Ecosystems LTER program (funded by OPP-1656026 and OPP-2322664) also provided travel support for E.B.'s field work, J.M. salary, and provided assistance with data archiving.

Additional Award Information:
Funder:National Science Foundation - Division of Biological Infrastructure
Funder ID:https://ror.org/04qn9mx93
Number:2022070
Title:BII-Implementation: The EMERGE Institute: Identifying EMergent Ecosystem Responses through Genes-to-Ecosystems Integration
URL:https://www.nsf.gov/awardsearch/showAward?AWD_ID=2022070
Additional Award Information:
Funder:National Science Foundation - Office of Polar Programs
Funder ID:https://ror.org/05nwjp114
Number:2322664
Title:LTER: Seasonal Controls and Emergent Effects of Changing Land-ice-ocean Interactions on Arctic Coastal Ecosystems (BLE II)
URL:https://www.nsf.gov/awardsearch/showAward?AWD_ID=2322664
Additional Award Information:
Funder:National Science Foundation - Office of Polar Programs
Funder ID:https://ror.org/05nwjp114
Number:1656026
Title:LTER: Beaufort Sea Lagoons: An Arctic Coastal Ecosystem in Transition
URL:https://www.nsf.gov/awardsearch/showAward?AWD_ID=1656026
Additional Award Information:
Funder:National Science Foundation - Office of Polar Programs
Funder ID:https://ror.org/05nwjp114
Number:1806213
Title:Collaborative Research: Causes and Consequences of Catastrophic Thermokarst Lake Drainage in an Evolving Arctic System
URL:https://www.nsf.gov/awardsearch/showAward?AWD_ID=1806213
Additional Award Information:
Funder:National Science Foundation - Office of Polar Programs
Funder ID:https://ror.org/05nwjp114
Number:1820883
Title:Collaborative Research: The Transition Zone of Upper Permafrost: The Frontline for Permafrost Changes across Climate and Landscape Gradients
URL:https://www.nsf.gov/awardsearch/showAward?AWD_ID=1820883
Additional Award Information:
Funder:National Science Foundation - Office of International Science and Engineering
Funder ID:https://ror.org/01k638r21
Number:1927553
Title:Collaborative Research: AccelNet: Permafrost Coastal Systems Network (PerCS-Net) -- A Circumpolar Alliance for Arctic Coastal Community Information Exchange
URL:https://www.nsf.gov/awardsearch/showAward?AWD_ID=1927553

Maintenance

Maintenance:
Description:No regular updates scheduled.
Frequency:notPlanned
Other Metadata

Additional Metadata

additionalMetadata
        |___text '\n      '
        |___element 'metadata'
        |     |___text '\n         '
        |     |___element 'replicationPolicy' in ns 'http://ns.dataone.org/service/types/v1' ('d1v1:replicationPolicy')
        |     |     |  \___attribute 'numberReplicas' = '1'
        |     |     |  \___attribute 'replicationAllowed' = 'true'
        |     |     |___text '\n            '
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        |     |     |     |___text 'urn:node:ARCTIC'
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        |___text '\n   '

Additional Metadata

additionalMetadata
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        |     |     |     |  \___attribute 'name' = 'centimeter'
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        |     |     |     |___text '\n               '
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        |     |     |     |  \___attribute 'unitType' = 'mass'
        |     |     |     |___text '\n               '
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        |     |     |     |     |___text 'unified atomic mass unit'
        |     |     |     |___text '\n            '
        |     |     |___text '\n            '
        |     |     |___element 'unit'
        |     |     |     |  \___attribute 'abbreviation' = 'degree'
        |     |     |     |  \___attribute 'id' = 'degree'
        |     |     |     |  \___attribute 'multiplierToSI' = '0.0174532924'
        |     |     |     |  \___attribute 'name' = 'degree'
        |     |     |     |  \___attribute 'parentSI' = 'radian'
        |     |     |     |  \___attribute 'unitType' = 'angle'
        |     |     |     |___text '\n               '
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        |     |     |     |     |___text '360 degrees comprise a unit circle.'
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        |     |     |___element 'unit'
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        |     |     |     |___text '\n               '
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        |     |     |        \___attribute 'id' = 'inverseNanometer'
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        |     |     |        \___attribute 'name' = 'inverseNanometer'
        |     |     |___text '\n            '
        |     |     |___element 'unit'
        |     |     |     |  \___attribute 'abbreviation' = 'L mg-1 m-1'
        |     |     |     |  \___attribute 'id' = 'literPerMilligramPerMeter'
        |     |     |     |  \___attribute 'name' = 'literPerMilligramPerMeter'
        |     |     |     |___text '\n               '
        |     |     |     |___element 'description'
        |     |     |     |     |___text 'liters per milligram per meter'
        |     |     |     |___text '\n            '
        |     |     |___text '\n            '
        |     |     |___element 'unit'
        |     |     |     |  \___attribute 'abbreviation' = 'mg g-1'
        |     |     |     |  \___attribute 'id' = 'milligramPerGram'
        |     |     |     |  \___attribute 'multiplierToSI' = '.001'
        |     |     |     |  \___attribute 'name' = 'milligramPerGram'
        |     |     |     |  \___attribute 'parentSI' = 'kilogramPerKilogram'
        |     |     |     |  \___attribute 'unitType' = 'massPerMass'
        |     |     |     |___text '\n               '
        |     |     |     |___element 'description'
        |     |     |     |     |___text 'milligrams per gram'
        |     |     |     |___text '\n            '
        |     |     |___text '\n            '
        |     |     |___element 'unit'
        |     |     |     |  \___attribute 'abbreviation' = 'mg_L'
        |     |     |     |  \___attribute 'id' = 'milligramsPerLiter'
        |     |     |     |  \___attribute 'multiplierToSI' = '0.001'
        |     |     |     |  \___attribute 'name' = 'milligramsPerLiter'
        |     |     |     |  \___attribute 'parentSI' = 'kilogramsPerCubicMeter'
        |     |     |     |  \___attribute 'unitType' = 'massDensity'
        |     |     |     |___text '\n               '
        |     |     |     |___element 'description'
        |     |     |     |     |___text 'milligrams / liter'
        |     |     |     |___text '\n            '
        |     |     |___text '\n            '
        |     |     |___element 'unit'
        |     |     |     |  \___attribute 'id' = 'number'
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        |     |     |     |  \___attribute 'unitType' = 'dimensionless'
        |     |     |     |___text '\n               '
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        |     |     |     |     |___text 'a number'
        |     |     |     |___text '\n            '
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        |     |     |     |  \___attribute 'id' = 'percent'
        |     |     |     |  \___attribute 'multiplierToSI' = '1'
        |     |     |     |  \___attribute 'name' = 'percent'
        |     |     |     |  \___attribute 'unitType' = 'dimensionless'
        |     |     |     |___text '\n               '
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        |     |     |     |___text '\n            '
        |     |     |___text '\n         '
        |     |___text '\n      '
        |___text '\n   '

EDI is a collaboration between the University of New Mexico and the University of Wisconsin – Madison, Center for Limnology:

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