Static chamber fluxes of carbon dioxide and methane from coastal wetlands on Upper Cape Cod, Massachusetts and supporting environmental data, 2021

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Frequently anticipated questions:


What does this data set describe?

Title:
Static chamber fluxes of carbon dioxide and methane from coastal wetlands on Upper Cape Cod, Massachusetts and supporting environmental data, 2021
Abstract:
Saline tidal wetlands are important sites of carbon sequestration and produce negligible methane (CH4) emissions due to regular inundation with sulfate-rich seawater. Yet, widespread management of coastal hydrology has restricted vast areas of coastal wetlands to tidal exchange. These ecosystems often undergo impoundment and freshening, which in turn cause vegetation shifts like invasion by Phragmites, that affect ecosystem carbon balance. Understanding controls of carbon exchange in these understudied ecosystems is critical for informing climate consequences of blue carbon restoration and/or management interventions. Here we present measurements of net ecosystem exchange of carbon dioxide (CO2) and methane, along with ancillary meteorological data, collected from coastal wetlands across Cape Cod to evaluate the effect of hydrological management and salinity on carbon exchange in coastal wetlands.
Supplemental_Information:
This dataset is a new addition to version 2 of this data release. For more information, see the following field activities: https://cmgds.marine.usgs.gov/fan_info.php?fan=2021-026-FA and https://cmgds.marine.usgs.gov/fan_info.php?fan=2022-011-FA
  1. How might this data set be cited?
    Sanders-DeMott, Rebecca, Eagle, Meagan J., Kroeger, Kevin D., Brooks, Thomas W., Jennifer A. O'Keefe Suttles, Nick, Sydney K., Mann, Adrian G., Kuhl, Sophie, and Gibson, Simone, 2022, Static chamber fluxes of carbon dioxide and methane from coastal wetlands on Upper Cape Cod, Massachusetts and supporting environmental data, 2021: data release DOI:10.5066/P9RRL3T0, U.S. Geological Survey, Coastal and Marine Hazards and Resources Program, Woods Hole Coastal and Marine Science Center, Woods Hole, MA.

    Online Links:

    This is part of the following larger work.

    Sanders-DeMott, Rebecca, Eagle, Meagan, Kroeger, Kevin, Wang, Faming, Brooks, T. Wallace, Jennifer A. O'Keefe Suttles, Nick, Sydney, Mann, Adrian, and Tang, Jianwu, 2022, Carbon dioxide and methane fluxes with supporting environmental data from coastal wetlands across Cape Cod, Massachusetts (ver 2.0, June 2022): data release DOI:10.5066/P9RRL3T0, U.S. Geological Survey, Reston, VA.

    Online Links:

    Other_Citation_Details:
    Suggested citation: Sanders-DeMott, R., Eagle, M.J., Kroeger, K.D., Wang, F., Brooks, T.W., O'Keefe Suttles, J.A., Nick, S.K., Mann, A.G., and Tang, J. 2022, Carbon dioxide and methane fluxes with supporting environmental data from coastal wetlands across Cape Cod, Massachusetts (ver 2.0, June 2022): U.S. Geological Survey data release, https://doi.org/10.5066/P9RRL3T0.
  2. What geographic area does the data set cover?
    West_Bounding_Coordinate: -70.6703
    East_Bounding_Coordinate: -70.4984
    North_Bounding_Coordinate: 41.6015
    South_Bounding_Coordinate: 41.5295
  3. What does it look like?
    https://www.sciencebase.gov/catalog/file/get/629fa3e2d34ec53d276fd537?name=phragmites_chamber.jpg&allowOpen=true (JPEG)
    Browse graphic is a photograph of a chamber sampling platform in a Phragmites wetland at Sage Lot Pond, Waquoit, MA.
  4. Does the data set describe conditions during a particular time period?
    Beginning_Date: 25-Apr-2021
    Ending_Date: 18-May-2022
    Currentness_Reference:
    Ground condition. These dates bracket the period of monthly sampling when the measurements were made.
  5. What is the general form of this data set?
    Geospatial_Data_Presentation_Form: tabular digital data
  6. How does the data set represent geographic features?
    1. How are geographic features stored in the data set?
      Indirect_Spatial_Reference:
      Geographic Names Information System (GNIS) placenames are included as keywords to give the general location of core collections. The entity contains attributes with specific latitude and longitude of each core collection; several attributes are also included to describe the core collection location (nearest body of water and vegetation type). Refer to the entity and attribute definitions for "site_name", "veg_type", "site_name", "status", and "sampling_location_name" for details.
      This is a Point data set. It contains the following vector data types (SDTS terminology):
      • Point
    2. What coordinate system is used to represent geographic features?
      Horizontal positions are specified in geographic coordinates, that is, latitude and longitude. Latitudes are given to the nearest 1.0E-5. Longitudes are given to the nearest 1.0E-5. Latitude and longitude values are specified in Decimal degrees. The horizontal datum used is North American Datum of 1983.
      The ellipsoid used is Geodetic Reference System 80.
      The semi-major axis of the ellipsoid used is 6378137.0.
      The flattening of the ellipsoid used is 1/298.257222101.
      Vertical_Coordinate_System_Definition:
      Altitude_System_Definition:
      Altitude_Datum_Name: North American Vertical Datum of 1988
      Altitude_Resolution: 0.001
      Altitude_Distance_Units: meters
      Altitude_Encoding_Method: Attribute values
  7. How does the data set describe geographic features?
    chamber_fluxes_2021.csv
    Comma Separated Value (CSV) file containing data on methane and carbon dioxide fluxes. This dataset has 216 records. (Source: Producer Defined)
    date
    Date the measurement was collected in the format yyyy-mm-dd. (Source: Producer Defined) Numeric value representing the date
    start_datetime
    Date and time that the chamber incubation was started in local standard time (UTC - 05:00) in the format yyyy-mm-dd hh:mm:ss. (Source: Producer Defined) Numeric value representing the date and time.
    end_datetime
    Date and time that the chamber incubation was ended in local standard time (UTC - 05:00) in the format yyyy-mm-dd hh:mm:ss. (Source: Producer Defined) Numeric value representing the date and time.
    site_name
    Site name of sampling location (Source: Producer Defined)
    ValueDefinition
    Sage Lot PondA site located within the Waquoit Bay National Estuarine Research Reserve in Waquoit, MA.
    Flat PondA site located within the Waquoit Bay National Estuarine Research Reserve in Waquoit, MA.
    Woods Hole ParkA site located in the village of Woods Hole, MA.
    Quaker Meeting HouseA site located within West Falmouth, MA.
    status
    Hydrological management status of the sampling location (Source: Producer Defined)
    ValueDefinition
    UnrestrictedIndicates that the sampling location experiences natural, unrestricted tidal exchange.
    ImpoundedIndicates that at this sampling location water is retained but tidal exchange is limited or excluded by infrastructure such as dikes, roads, or culverts.
    veg_type
    Dominant vegetation at sampling location (Source: Producer Defined)
    ValueDefinition
    Phragmites WetlandSampling location is a wetland dominated by Phragmites australis
    Typha/Schoenoplectus WetlandSampling location is a wetland dominated by Typha latifolia and Schoenoplectus
    sampling_location_name
    Sampling location name indicating both the hydrological management and salinity status relative to the geographical site as referenced in the related publication (Sanders-DeMott and others, 2022) (Source: Producer Defined)
    ValueDefinition
    Unrestricted-HighSampling location that experiences natural, unrestricted tidal exchange and is the high salinity plot of the site pair at Sage Lot Pond as referenced in the related publication (Sanders-DeMott and others, 2022)
    Unrestricted-LowSampling location that experiences natural, unrestricted tidal exchange and is the low salinity plot of the site pair at Sage Lot Pond as referenced in the related publication (Sanders-DeMott and others, 2022)
    Impounded-FPPSampling location that experiences tidal exchange that is limited or excluded and is located in a Phrgamites stand at Flat Pond
    Impounded-FPTSSampling location that experiences tidal exchange that is limited or excluded and is located in a mixed Typha latifolia and Schoenoplectus stand at Great Flat Pond
    Impounded-WHSampling location that experiences tidal exchange that is limited or excluded and is located in Woods Hole Park in Woods Hole, MA
    Impounded-QMHSampling location that experiences tidal exchange that is limited or excluded and is located on Quaker Meeting House property in West Falmouth, MA
    chamber_rep
    Identifier of the chamber replicate at each sampling location (Source: Producer Defined)
    Range of values
    Minimum:1
    Maximum:3
    latitude
    Latitude decimal degrees north, NAD83 (Source: Producer Defined)
    Range of values
    Minimum:41.52952
    Maximum:41.60149
    Units:decimal degrees
    longitude
    Longitude decimal degrees west, NAD83. The negative value indicates a location in the western hemisphere. (Source: Producer Defined)
    Range of values
    Minimum:-70.67031
    Maximum:-70.49842
    Units:decimal degrees
    elevation
    Elevation relative to NAVD88 datum in meters. (Source: Producer Defined)
    Range of values
    Minimum:0.15
    Maximum:1.36
    Units:meters
    chamber_transparency
    Indicator of whether chamber incubation was conducted with transparent chamber to allow light exposure or opaque chamber to block out light. (Source: Producer Defined)
    ValueDefinition
    opaqueChamber incubation conducted with an opaque cover to block out sunlight and assess fluxes in the dark.
    transparentChamber incubation conducted with a transparent chamber to allow sunlight and assess fluxes in the light.
    CH4_flux
    Flux of methane calculated from the slope of CH4 concentration change in nanomoles of CH4 per square meter per second (nmol CH4 m-2 sec-1). Positive values indicate a flux of methane out of the ecosystem into the atmosphere and negative values indicate a flux out of the atmosphere into the ecosystem. (Source: Producer Defined)
    Range of values
    Minimum:0.38
    Maximum:587.62
    Units:nmol CH4 m-2 sec-1
    CH4_flux_ebullition
    Flux of methane calculated in nanomoles of CH4 per square meter per second (nmol CH4 m-2 sec-1) when ebullition was suspected. Calculation is based on the difference between initial and final concentration as applicable when ebullition was suspected due to non-linear changes in CH4 concentration during incubation. Positive values indicate a flux of methane out of the ecosystem into the atmosphere and negative values indicate a flux out of the atmosphere into the ecosystem. (Source: Producer Defined)
    ValueDefinition
    empty cellNo ebullition was observed
    Range of values
    Minimum:49.16
    Maximum:344.48
    Units:nmol CH4 m-2 sec-1
    CO2_flux
    Flux of carbon dioxide calculated from the slope of CO2 concentration change in micromoles of CO2 per square meter per second (umol CO2 m-2 sec-1). Positive values indicate a flux of CO2 out of the ecosystem into the atmosphere and negative values indicate a flux out of the atmosphere into the ecosystem. (Source: Producer Defined)
    Range of values
    Minimum:-24.92
    Maximum:21.29
    Units:umol CO2 m-2 sec-1
    soil_moisture
    Soil volumetric water content (VWC) in percent integrated over the top 5 cm of soil. Measured with handheld Meter Group Inc., TEROS-10 just outside each collar after gas sampling. (Source: Producer Defined)
    ValueDefinition
    empty cellNo measurement recorded due to flooded surface
    Range of values
    Minimum:32
    Maximum:74.1
    Units:percent
    salinity
    Salinity in practical salinity units (psu) at time of chamber sampling measured within 2 meters of chamber collar in a ~30 cm deep 3 cm-diameter PVC well screened from 0 to 20 cm depth and equipped to continuously (15-minute intervals) monitor water-table depth relative to the soil surface, salinity, and water temperature (In-Situ Inc., Aqua TROLL 200). This is a specific subsample of a larger time series dataset. Full dataset available in O'Keefe Suttles and others, 2022.
    O'Keefe Suttles, J.A., Eagle, M.J., Sanders-DeMott, R., Nick, S.K., Brooks, T.W., Mann, A.G., and Kroeger, K.D., 2022, Continuous water level, salinity, and temperature data from coastal wetland monitoring wells, Cape Cod, Massachusetts: U.S. Geological Survey data release, https://doi.org/10.5066/P9T1KOTW. (Source: Producer Defined)
    Range of values
    Minimum:0.143
    Maximum:23.916
    Units:psu
    dbs
    Water table depth relative to the soil surface in meters (where negative values indicate water level is below the soil surface and positive values indicate flooded conditions with water table above the soil surface) at time of chamber sampling. Measurements were within 2 meters of chamber collar in a ~30 cm deep 3 cm-diameter PVC well screened from 0 to 20 cm depth and equipped to continuously (15-minute intervals) monitor water-table depth relative to the soil surface, salinity, and water temperature (In-Situ Inc., Aqua TROLL 200). This is a specific subsample of a larger time series dataset. Full dataset available in O'Keefe Suttles and others, 2022.
    O'Keefe Suttles, J.A., Eagle, M.J., Sanders-DeMott, R., Nick, S.K., Brooks, T.W., Mann, A.G., and Kroeger, K.D., 2022, Continuous water level, salinity, and temperature data from coastal wetland monitoring wells, Cape Cod, Massachusetts: U.S. Geological Survey data release, https://doi.org/10.5066/P9T1KOTW. (Source: Producer Defined)
    Range of values
    Minimum:-0.172
    Maximum:0.267
    Units:meters
    water_temp
    Water temperature in degrees Celsius at time of chamber sampling measured within 2 meters of chamber collar in a ~30 cm deep 3 cm-diameter PVC well screened from 0 to 20 cm depth and equipped to continuously (15-minute intervals) monitor water-table depth relative to the soil surface, salinity, and water temperature (In-Situ Inc., Aqua TROLL 200). This is a specific subsample of a larger time series dataset. Full dataset available in O'Keefe Suttles and others, 2022.
    O'Keefe Suttles, J.A., Eagle, M.J., Sanders-DeMott, R., Nick, S.K., Brooks, T.W., Mann, A.G., and Kroeger, K.D., 2022, Continuous water level, salinity, and temperature data from coastal wetland monitoring wells, Cape Cod, Massachusetts: U.S. Geological Survey data release, https://doi.org/10.5066/P9T1KOTW. (Source: Producer Defined)
    Range of values
    Minimum:12.5
    Maximum:20.053
    Units:degrees Celsius
    soil_temp
    Soil temperature in degrees Celsius measured at 10 cm depth below the soil surface at the time of chamber sampling. This is a specific subsample of a larger time series dataset. Full dataset available in air_soil_temp_2021-2022.csv (part of this data release). (Source: Producer Defined)
    Range of values
    Minimum:13.016
    Maximum:21.62
    Units:degrees Celsius
    air_temp
    Air temperature in degrees Celsius measured at 1 m height above the soil surface at the time of chamber sampling. This is a specific subsample of a larger time series dataset. Full dataset available in air_soil_temp_2021-2022.csv (part of this data release) (Source: Producer Defined)
    Range of values
    Minimum:18.96
    Maximum:32.0
    Units:degrees Celsius
    par
    Photosynthetically active radiation (PAR) in micromoles photons per meter squared per second (umol photons m-2 sec-1) at the time of chamber sampling. (Source: Producer Defined)
    Range of values
    Minimum:164.1
    Maximum:2131.2
    Units:umol photons m-2 sec-1
    air_soil_temp_2021-2022.csv
    Comma Separated Value (CSV) file containing data on soil and air temperature. The dataset has 307729 records. (Source: Producer Defined)
    datetime
    Date and time that sensor measurement was logged in local standard time (UTC - 05:00) in the format yyyy-mm-dd hh:mm:ss. (Source: Producer Defined) A numeric value representing date and time.
    site_name
    Site name of sampling location (Source: Producer Defined)
    ValueDefinition
    Sage Lot PondA site located within the Waquoit Bay National Estuarine Research Reserve in Waquoit, MA.
    Flat PondA site located within the Waquoit Bay National Estuarine Research Reserve in Waquoit, MA.
    Woods Hole ParkA site located in the village of Woods Hole, MA.
    Quaker Meeting HouseA site located within West Falmouth, MA.
    Herring RiverA site located within the Cape Cod National Seashore in Wellfleet, MA.
    status
    Hydrological management status of the sampling location (Source: Producer Defined)
    ValueDefinition
    UnrestrictedIndicates that the sampling location experiences natural, unrestricted tidal exchange.
    ImpoundedIndicates that at this sampling location water is retained but tidal exchange is limited or excluded by infrastructure such as dikes, roads, or culverts
    veg_type
    Dominant vegetation at sampling location (Source: Producer Defined)
    ValueDefinition
    Phragmites WetlandSampling location is a wetland dominated by Phragmites australis
    Typha/Schoenoplectus WetlandSampling location is a wetland dominated by Typha lattifolia and Schoenoplectus
    sampling_location_name
    Sampling location name indicating both the hydrological management and salinity status relative to the geographical site as referenced in the related publication (Sanders-DeMott and others, 2022) (Source: Producer Defined)
    ValueDefinition
    Unrestricted-HighSampling location that experiences natural, unrestricted tidal exchange and is the high salinity plot of the site pair at Sage Lot Pond as referenced in the related publication (Sanders-DeMott and others, 2022)
    Unrestricted-LowSampling location that experiences natural, unrestricted tidal exchange and is the low salinity plot of the site pair at Sage Lot Pond as referenced in the related publication (Sanders-DeMott and others, 2022)
    Impounded-FPPSampling location that experiences tidal exchange that is limited or excluded and is located in a Phragamites stand at Flat Pond
    Impounded-FPTSSampling location that experiences tidal exchange that is limited or excluded and is located in a mixed Typha latifolia and Schoenoplectus stand at Flat Pond
    Impounded-WHSampling location that experiences tidal exchange that is limited or excluded and is located in Woods Hole Park in Woods Hole, MA
    Impounded-QMHSampling location that experiences tidal exchange that is limited or excluded and is located on Quaker Meeting House property in West Falmouth, MA
    Impounded-HighSampling location that experiences tidal exchange that is limited or excluded and is the high salinity plot of the site pair at Herring River as referenced in the related publication (Sanders-DeMott and others, 2022)
    Impounded-LowSampling location that experiences tidal exchange that is limited or excluded and is the low salinity plot of the site pair at Herring River as referenced in the related publication (Sanders-DeMott and others, 2022)
    latitude
    Latitude decimal degrees north, NAD83 (Source: Producer Defined)
    Range of values
    Minimum:41.52952
    Maximum:41.93784
    Units:decimal degrees
    longitude
    Longitude decimal degrees west, NAD83. The negative value indicates a location in the western hemisphere. (Source: Producer Defined)
    Range of values
    Minimum:-70.67029
    Maximum:-70.05472
    Units:decimal degrees
    air_temp_1m
    Air temperature recorded at 1 meter height above the sediment surface (Source: Producer Defined)
    ValueDefinition
    empty cellNo Data due to instrument malfunction
    Range of values
    Minimum:-20.9
    Maximum:39.0
    Units:degrees Celsius
    soil_temp
    Soil temperature recorded at 10 cm depth below the sediment surface (Source: Producer Defined)
    ValueDefinition
    empty cellNo Data due to instrument malfunction
    Range of values
    Minimum:0.9
    Maximum:24.8
    Units:degrees Celsius
    sensor
    Sensor manufacturer and model (Source: Producer Defined)
    ValueDefinition
    HOBO U23-003 Temp/TempManufacturer and model of sensor used to record both air and soil temperature
    HOBO MX2303 Temp/TempManufacturer and model of sensor used to record both air and soil temperature
    slp_met_2021-2022.csv
    Comma Separated Value (CSV) file containing meteorological data. This dataset has 36069 records. (Source: Producer Defined)
    datetime
    Date and time that sensor measurement was logged in local standard time (UTC - 05:00) in the format yyyy-mm-dd hh:mm:ss. (Source: Producer Defined) A numeric value representing date and time.
    site_name
    Site of the sampling location (Source: Producer Defined)
    ValueDefinition
    Sage Lot PondA site located within the Waquoit Bay National Estuarine Research Reserve in Waquoit, MA.
    status
    Hydrological management status of the sampling location (Source: Producer Defined)
    ValueDefinition
    UnrestrictedIndicates that the sampling location experiences natural, unrestricted tidal exchange.
    veg_type
    Dominant vegetation at sampling location (Source: Producer Defined)
    ValueDefinition
    Phragmites WetlandSampling location is a wetland dominated by Phragmites australis
    latitude
    Latitude decimal degrees north, NAD83 (Source: Producer Defined)
    Range of values
    Minimum:41.55773
    Maximum:41.55773
    Units:decimal degrees
    longitude
    Longitude decimal degrees west, NAD83. The negative value indicates a location in the western hemisphere. (Source: Producer Defined)
    Range of values
    Minimum:-70.50443
    Maximum:-70.50443
    Units:decimal degrees
    air_temp_3m
    Air temperature recorded at 3 meters height above the sediment surface with Onset HOBO Temperature/RH Smart Sensor S-THB-M00x (Source: Producer Defined)
    ValueDefinition
    empty cellNo Data due to instrument malfunction.
    Range of values
    Minimum:-12.6
    Maximum:33.9
    Units:degrees Celsius
    RH
    Relative humidity recorded at 3 meters height above the sediment surface with Onset HOBO Temperature/RH Smart Sensor S-THB-M00x (Source: Producer Defined)
    ValueDefinition
    empty cellNo Data due to instrument malfunction.
    Range of values
    Minimum:20.5
    Maximum:100.0
    Units:percent
    PAR
    Incoming photosynthetically active radiation (PAR) in micromoles photons per meter squared per second (umol photons m-2 sec-1) recorded at 3 meters height above the sediment surface with Onset HOBO Photosynthetically Active Radiation Smart Sensor S-LIA-M003 (Source: Producer Defined)
    ValueDefinition
    empty cellNo Data due to instrument malfunction.
    Range of values
    Minimum:1.2
    Maximum:2511.2
    Units:umol photons m-2 sec-1

Who produced the data set?

  1. Who are the originators of the data set? (may include formal authors, digital compilers, and editors)
    • Rebecca Sanders-DeMott
    • Meagan J. Eagle
    • Kevin D. Kroeger
    • Thomas W. Brooks
    • Jennifer A. O'Keefe Suttles
    • Sydney K. Nick
    • Adrian G. Mann
    • Sophie Kuhl
    • Simone Gibson
  2. Who also contributed to the data set?
  3. To whom should users address questions about the data?
    Rebecca Sanders-Demott
    U.S. Geological Survey, NORTHEAST REGION
    384 Woods Hole Road
    Woods Hole, MA
    US

    508-548-8700 x2255 (voice)
    rsanders-demott@usgs.gov

Why was the data set created?

Measurements of carbon dioxide and methane fluxes from static chambers were collected in 2021 to assess carbon exchange at coastal wetland sites across a range of impounded and natural, tidally unrestricted conditions in several villages within Falmouth, MA that vary in salinity, management status, and water level. Environmental metrics that could inform carbon exchange, including air and soil temperature, and photosynthetically active radiation were also collected to support data interpretation. This dataset can help evaluate the effect of hydrologic management on carbon dioxide and methane exchange in coastal wetlands. Data were collected to inform predictive models of carbon fluxes across coastal wetlands of varying management status and salinity and to facilitate National Park Service restoration planning and future blue carbon project assessments.

How was the data set created?

  1. From what previous works were the data drawn?
  2. How were the data generated, processed, and modified?
    Date: 15-Oct-2021 (process 1 of 6)
    Six sampling locations were established across several villages of Falmouth, MA for static chamber sampling. Two sampling locations were established at a site with natural, unrestricted tidal exchange at Sage Lot Pond, two in an impounded marsh at Flat Pond, one site in West Falmouth behind a Quaker Meeting House, and one site in Woods Hole behind Woods Hole Park. Each sampling location was equipped with three replicate collars for static chamber measurements and one pair of air/soil temperature sensors. The two sites at Sage Lot Pond were part of a prior study established in 2020 and data collected in 2020 from those sites is available at https://www.sciencebase.gov/catalog/item/62557ae8d34e21f8276f4879.
    To facilitate static chamber CH4 and CO2 flux measurements, round PVC collars (55 cm inner diameter, 24 cm height, 3 replicates per sampling location (n = 6)) were inserted into the sediment surrounding intact vegetation to a depth of at least 10 cm more than four weeks prior to initial sampling to allow the soil to equilibrate from disturbance. On each sample collection date, we used a modular system of clear, round acrylic chambers to enclose the vegetation and sediment surface for flux measurement. Chamber sections were 55 cm diameter and 0.91 meters (m) tall. Depending on the height of the vegetation at the sampling location we used either one, two, or three stacked chambers for a total chamber height of 0.91, 1.83 or 2.74 m and empty chamber volume of 0.22, 0.43 or 0.64 cubic meters (m3). The topmost chamber always had a transparent lid permanently affixed with silicone caulking and a vent tube to allow for pressure equilibration. Two battery-powered fans (10 cm in diameter) were attached to the inside of the chamber to homogenize air and temperature sensors (HOBO TidbiT v2, Onset Computer Corporation) were mounted to the inside of the top and bottom chambers to record chamber air temperature. All samples were collected during mid-day hours between 10:00-14:00 local standard time. Chamber air was considered equilibrated based on visual inspection of the stability of a linear concentration change in the gases of interest, this was typically less than 60 seconds.
    Field data required to calculate fluxes (i.e., chamber head space, chamber deployment time) were recorded on field datasheets and later entered into electronic spreadsheets. Concentrations of CH4 and CO2 during 2-5 minutes incubations were measured and recorded using a portable optical feedback-cavity enhanced absorption spectrometer (LI-7810 CH4/CO2/H2O Trace Gas Analyzer, LI-COR, Inc.) sampling at 1 Hz. Chamber flux incubations were conducted both in the light with transparent chambers to quantify net ecosystem exchange, and in the dark with opaque covering of the chambers to quantify ecosystem respiration in the absence of photosynthesis.
    We used a sliding regression (“rollRegres” package in R, Christoffersen, 2019) to identify the 120-second window during the incubation where a simple linear regression of CH4 or CO2 concentration by time had a maximum R2. We verified that all linear models used to calculate flux had a significant slope (p less than 0.001) and an RMSE ≤ 1 ppm for CO2 and ≤ 10 ppb for CH4. Four CO2 measurements did not have a slope significantly different than 0, and therefore those fluxes were set to 0. Three additional CO2 measurements were rejected for low R2 and RMSE > 1 ppm.
    We also assessed each incubation for non-linear changes in CH4 concentration over time as a signal of potential ebullition. When potential ebullition was observed, in addition to applying the sliding regression described above, we estimated CH4 concentration change based on the initial and final concentration of CH4 gas (VCS, 2015).
    The rate of concentration change of CO2 and CH4 (slope or the difference between final and initial when ebullition was suspected) was converted to an area-based flux using the Ideal Gas Law and the volume and footprint of the chamber, along with measured chamber air temperature (pooled across the two temperature sensors). Calculations were executed with the “conc_to_flux” function in the R package “ecoflux” (Shannon, 2018).
    This process step and all subsequent process steps (unless otherwise noted) were performed by the same person, Rebecca Sanders-Demott.
    Christoffersen, B., 2019, rollRegres: Fast Rolling and Expanding Window Linear Regression. R package version 0.1.3. https://CRAN.R-project.org/package=rollRegres
    Shannon, J., 2018, ecoFlux: Functions for ecological flux studies including sap flux and soil/stem C efflux (0.3.1). https://rdrr.io/github/jpshanno/ecoflux/
    Verified Carbon Standard (VCS), 2015, Approved VCS Methodology VM 0033: Methodology for Tidal Wetland and Seagrass Restoration. Version 1.0, 20 November 2015, Sectoral Scope 14. Developed by Verra with Restore America’s Estuaries and Silvestrum. 1–115. https://verra.org/wp-content/uploads/2018/03/VM0033-Tidal-Wetland-and-Seagrass-Restoration-v1.0.pdf Person who carried out this activity:
    Rebecca Sanders-Demott
    U.S. Geological Survey, NORTHEAST REGION
    384 Woods Hole Road
    Woods Hole, MA
    US

    508-548-8700 x2255 (voice)
    rsanders-demott@usgs.gov
    Date: 15-Oct-2021 (process 2 of 6)
    Soil volumetric water content (VWC) integrated over the top 5 cm was measured (Meter Group Inc., TEROS-10) just outside each collar after gas sampling. Values were recorded by hand on a field data sheet and later entered into an electronic spreadsheet.
    Date: 15-Oct-2021 (process 3 of 6)
    Photosynthetically active radiation (PAR) was measured concurrent with chamber sampling with a PAR sensor (Onset Photosynthetically Active Radiation (PAR) Smart Sensor, model S-LIA-M003) deployed on a portable 4-meter tall tripod mast that was set up adjacent to each site during sampling. Data were logged every 1 minute from the time we arrived on site until chamber sampling was completed on an Onset HOBO USB Microstation Logger. When daily sampling was completed, data files were downloaded to a field laptop via HOBOware software (version 3.7.2.1), converted to .csv files, and matched by timestamp to the chamber incubation data via R.
    Date: 18-May-2022 (process 4 of 6)
    At each chamber sampling location, the three replicate collars were paired with one soil temperature sensor (10 cm depth) and one air temperature sensor (1 m height) mounted on a PVC well in April 2021. Air and soil temperature were logged every 15 minutes. Raw data files were downloaded in the field monthly. Ultimately all data were uploaded as .hobo files to the Woods Hole Coastal and Marine Science Center (WHCMSC) network server. Raw data files were converted to CSV files in the software: HOBOware (version 3.7.2.1). Data were plotted to check for any irregularities in sensor functioning (e.g. outliers or unrealistic values). All found irregularities were removed from the final dataset.
    Date: 18-Nov-2021 (process 5 of 6)
    Latitude and longitude of each chamber and sensor location, along with elevation of chambers was measured with a Trimble Real-Time Kinematic (RTK) GPS. Accuracy was 2-3 cm according to instrument corrections. Data files were exported from the instrument via a .csv file and appended to the data files of calculated fluxes or sensors via R.
    Date: 15-Apr-2022 (process 6 of 6)
    After all chamber flux data were finalized, we exported the sensor data (logged at 15-minute intervals) that most closely matched the timestamp of the chamber incubation and appended those values to the chamber fluxes data table using R for user convenience. Sensor data included are air and soil temperature described here and availanble in the file air_soil_temp_2021-2022.csv (part of this data release), as well as data on water temperature, water table depth below surface, and salinity, which are available in O'Keefe Suttles and others, 2022.
    O'Keefe Suttles, J.A., Eagle, M.J., Sanders-DeMott, R., Nick, S.K., Brooks, T.W., Mann, A.G., and Kroeger, K.D., 2022, Continuous water level, salinity, and temperature data from coastal wetland monitoring wells, Cape Cod, Massachusetts: U.S. Geological Survey data release, https://doi.org/10.5066/P9T1KOTW.
  3. What similar or related data should the user be aware of?
    Sanders-DeMott, Rebecca, Eagle, Meagan J., Kroeger, Kevin D., Wang, Faming, Brooks, Thomas W., O'Keefe Suttles, Jennifer A., Nick, Sydney K., Mann, Adrian G., and Tang, Jianwu, 2022, Impoundment increases methane emissions in Phragmites-invaded coastal wetlands: Global Change Biology DOI:10.1111/gcb.16217, Wiley, Hoboken, New Jersey.

    Online Links:

    Other_Citation_Details:
    Journal article based on prior data from some of the sampling locations included in this data release.
    Jennifer A. O'Keefe Suttles, Eagle, Meagan J., Sanders-DeMott, Rebecca, Nick, Sydney K., Brooks, Thomas W., Mann, Adrian G., and Kroeger, Kevin D., 2022, Continuous Water Level, Salinity, and Temperature Data from Coastal Wetland Monitoring Wells, Cape Cod, Massachusetts: data release DOI:10.5066/P9T1KOTW, U.S. Geological Survey, Reston, VA.

    Online Links:

    Other_Citation_Details:
    Provides continuous data on water level, salinity, and water temperature concurrent with chamber flux measurements presented in this data release.

How reliable are the data; what problems remain in the data set?

  1. How well have the observations been checked?
    The LI-7810 CH4/CO2/H2O Trace Gas Analyzer has a precision of 0.60 parts per billion (ppb) at 2 parts per million (ppm) with 1 second averaging for methane (CH4) and of 3.5 ppm at 400 ppm with 1 second averaging for carbon dioxide (CO2). The instrument calibration was checked using laboratory calibration gases prior to field measurements in spring 2020. All calculated slopes used to calculate fluxes were subject to statistical checks as outlined in Process Step 1. Each sampling location was measured in triplicate for gas fluxes and with ten replicates for biomass assessments to reduce uncertainty. Manufacturer's specifications for the dual channel temperature logger (used in this study for continuous measurement of soil and air (-10 cm and 1 m respectively from land surface; Onset, model type HOBO U23 Pro v2 and MX2303) for accuracy is +/- 0.21 degrees Celsius from 0 degrees Celsius to 50 degrees Celsius; the manufacturer's specification for resolution is 0.02 degrees Celsius at 25 degrees Celsius. Accuracy of the photosynthetically active raditation (PAR) sensor +/- 5 micromoles per meter squared per second and resolution of the PAR sensor is 2.5 micromoles per meter squared per second. Relative humidty (RH) sensor was enclosed within a solar radiation shield and deployed on a mast with other meteorological sensors. Typical accuracy of the RH sensor is +/-2.5 percent and resolution is 0.1 percent RH. No formal attribute accuracy tests were conducted.
  2. How accurate are the geographic locations?
    Latitude and Longitude were measured for each of the chamber gas sampling collars (3 per sampling location) and the paired soil and air temperature sensors (1 per sampling location) by Trimble Real-Time Kinematic (RTK) GPS at the end of the sampling season. Recorded Horizontal Dilution of Precision (HDOP) was 0.600 or less for all measurements. Average horizontal accuracy of this method is +/- 30 centimeters. No formal positional accuracy tests were conducted.
  3. How accurate are the heights or depths?
    Land surface elevations were measured for each of the chamber gas sampling collars (3 per sampling location) and the paired soil and air temperature sensors (1 per sampling location) by Trimble Real-Time Kinematic (RTK) GPS at the end of the sampling season. Recorded Vertical Dilution of Precision (VDOP) was 0.900 or less for all measurements. Average vertical accuracy of this method is +/- 5 centimeters. No formal positional accuracy tests were conducted.
  4. Where are the gaps in the data? What is missing?
    Gaps in the continuous data record for a given parameter may have been the result of one of several sources: sensor not deployed during that time period, vandalism of an instrument by humans or destruction by chewing animals, removal of an instrument for maintenance, corrupt data file due to malfunctioning instrument, or data excluded based on quality assessment described in process step. Exclusions of data from the continuous record are coded as blank cells.
  5. How consistent are the relationships among the observations, including topology?
    Each logged parameter set was queried for maximum and minimum values to be sure logged data fell within expected ranges for the environmental conditions.

How can someone get a copy of the data set?

Are there legal restrictions on access or use of the data?
Access_Constraints None. Please see 'Distribution Info' for details.
Use_Constraints None. Users are advised to read the dataset's metadata thoroughly to understand appropriate use and data limitations.
  1. Who distributes the data set? (Distributor 1 of 1)
    ScienceBase
    U.S. Geological Survey
    Denver Federal Center, Building 810, Mail Stop 302
    Denver, CO
    United States

    1-888-275-8747 (voice)
    sciencebase@usgs.gov
  2. What's the catalog number I need to order this data set? The dataset contains three CSV files containing the data (chamber_fluxes_2021.csv; air_soil_temp_2021-2022.csv; slp_met_2021-2022.csv), the browse graphic (phragmites_chamber.jpg), and the FGDC CSDGM metadata in XML format.
  3. What legal disclaimers am I supposed to read?
    Neither the U.S. Government, the Department of the Interior, nor the USGS, nor any of their employees, contractors, or subcontractors, make any warranty, express or implied, nor assume any legal liability or responsibility for the accuracy, completeness, or usefulness of any information, apparatus, product, or process disclosed, nor represent that its use would not infringe on privately owned rights. The act of distribution shall not constitute any such warranty, and no responsibility is assumed by the USGS in the use of these data or related materials. Any use of trade, product, or firm names is for descriptive purposes only and does not imply endorsement by the U.S. Government.
  4. How can I download or order the data?
  5. What hardware or software do I need in order to use the data set?
    The data release includes 3 comma-delimited text files. The user must have software capable of opening the text file and reading the data formats.

Who wrote the metadata?

Dates:
Last modified: 15-Jun-2022
Metadata author:
Rebecca Sanders-Demott
U.S. Geological Survey, NORTHEAST REGION
384 Woods Hole Road
Woods Hole, MA
US

508-548-8700 x2255 (voice)
whsc_data_contact@usgs.gov
Contact_Instructions:
The metadata contact email address is a generic address in the event the person is no longer with USGS.
Metadata standard:
Content Standard for Digital Geospatial Metadata (FGDC-STD-001-1998)

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