Continuous water quality sensor data were collected at USGS 292939089544400 Wilkinson Bayou cutoff north of Wilkinson Bay, LA gage. Field water-quality measurements were collected using a YSI EXO2 water-quality sonde equipped with a data logger to capture hourly data using sensors for measuring water temperature, specific conductance, salinity, pH, oxidation and reduction potential (ORP), fluorescent dissolved organic matter (fDOM), and turbidity. The monitor was housed in an 8-inch diameter polyvinyl chloride (PVC) pipe attached to a temporary wooden structure near the gage. Measurements were collected from a fixed mid-depth point in the water column. All data were collected using U.S. Geological Survey (USGS) protocols and data are stored in the National Water Information System (NWIS) database. Records processing of measurement results for fouling and drift corrections of the data followed the USGS Techniques and Methods for continuous water-quality monitors (Wagner, et al., 2006), except for ORP and drift corrections for fDOM. ORP were uncorrected and were reported from the sonde directly. fDOM was evaluated for drift using periodic side by side comparisons with a new factory calibrated sensor to check for lamp degradation in the sensor and calibration checks were performed using onsite prepared fDOM standard. fDOM data have not been corrected for temperature, turbidity, or inner-filter effects (Booth et al., 2023). Turbidity drift corrections were applied using Wagner et al. (2006) except in some cases where it was determined not helpful to apply the correction based on unstable site conditions during the site visit. Sample results from July of 2019 to May 2022 are reported in this data release. Booth, A., Fleck, J., Pellerin, B.A., Hansen, A., Etheridge, A., Foster, G.M., Graham, J.L., Bergamaschi, B.A., Carpenter, K.D., Downing, B.D., Rounds, S.A., and Saraceno, J., 2023, Field techniques for fluorescence measurements targeting dissolved organic matter, hydrocarbons, and wastewater in environmental waters: Principles and guidelines for instrument selection, operation and maintenance, quality assurance, and data reporting: U.S. Geological Survey Techniques and Methods, book 1, chap. D11, 41 p., https://doi.org/10.3133/tm1D11. Wagner, R.J., Boulger, R.W., Jr., Oblinger, C.J., and Smith, B.A., 2006, Guidelines and standard procedures for continuous water-quality monitors—Station operation, record computation, and data reporting: U.S. Geological Survey Techniques and Methods 1–D3, 51 p. + 8 attachments; accessed August 3, 2022, at https://pubs.usgs.gov/tm/2006/tm1D3/pdf/TM1D3.pdf.

Continuous water quality sensor data were collected at USGS 292939089544400 Wilkinson Bayou cutoff north of Wilkinson Bay, LA gage. Field water quality measurements were collected using a YSI EXO2 water quality sonde equipped with a data logger to capture hourly data using sensors for measuring water temperature, specific conductance, salinity, pH, oxidation and reduction potential (ORP), fluorescent dissolved organic matter (fDOM), turbidity, and dissolved oxygen (DO). The monitor was housed in an 8-inch diameter polyvinyl chloride (PVC) pipe attached to a temporary wooden structure near the gage. Measurements were collected from a fixed mid-depth point in the water column. All data were collected using U.S. Geological Survey (USGS) protocols and data are stored in the National Water Information System (NWIS) database. Records processing of measurement results for fouling and drift corrections of the data followed the USGS Techniques and Methods for continuous water-quality monitors (Wagner et al., 2006), except for ORP and drift corrections for fDOM. ORP were uncorrected and were reported from the sonde directly. fDOM was evaluated for drift using periodic side-by-side comparisons with a new factory-calibrated sensor to check for lamp degradation in the sensor, and calibration checks were performed using on-site prepared fDOM standard. fDOM data have not been corrected for temperature, turbidity, or inner-filter effects (Booth et al., 2023). Turbidity drift corrections were applied using Wagner et al. (2006) except in some cases where it was determined not helpful to apply the correction based on unstable site conditions during the site visit. Sample results from June of 2022 to October 2023 are reported in this data release. References: Booth, A., Fleck, J., Pellerin, B.A., Hansen, A., Etheridge, A., Foster, G.M., Graham, J.L., Bergamaschi, B.A., Carpenter, K.D., Downing, B.D., Rounds, S.A., and Saraceno, J., 2023, Field techniques for fluorescence measurements targeting dissolved organic matter, hydrocarbons, and wastewater in environmental waters: Principles and guidelines for instrument selection, operation and maintenance, quality assurance, and data reporting: U.S. Geological Survey Techniques and Methods, book 1, chap. D11, 41 p., https://doi.org/10.3133/tm1D11. Wagner, R.J., Boulger, R.W., Jr., Oblinger, C.J., and Smith, B.A., 2006, Guidelines and standard procedures for continuous water-quality monitors—Station operation, record computation, and data reporting: U.S. Geological Survey Techniques and Methods 1–D3, 51 p. + 8 attachments; accessed August 3, 2022, at https://pubs.usgs.gov/tm/2006/tm1D3/pdf/TM1D3.pdf.

Continuous water quality sensor data were collected at USGS 292939089544400 Wilkinson Bayou cutoff north of Wilkinson Bay, LA gage. Field water-quality measurements were collected using a YSI EXO2 water-quality sonde equipped with a data logger to capture hourly data using sensors for measuring water temperature, specific conductance, salinity, pH, oxidation and reduction potential (ORP), fluorescent dissolved organic matter (fDOM), and turbidity. The monitor was housed in an 8-inch diameter polyvinyl chloride (PVC) pipe attached to a temporary wooden structure near the gage. Measurements were collected from a fixed mid-depth point in the water column. All data were collected using U.S. Geological Survey (USGS) protocols and data are stored in the National Water Information System (NWIS) database. Records processing of measurement results for fouling and drift corrections of the data followed the USGS Techniques and Methods for continuous water-quality monitors (Wagner, et al., 2006), except for ORP and drift corrections for fDOM. ORP were uncorrected and were reported from the sonde directly. fDOM was evaluated for drift using periodic side by side comparisons with a new factory calibrated sensor to check for lamp degradation in the sensor and calibration checks were performed using onsite prepared fDOM standard. fDOM data have not been corrected for temperature, turbidity, or inner-filter effects (Booth et al., 2023). Turbidity drift corrections were applied using Wagner et al. (2006) except in some cases where it was determined not helpful to apply the correction based on unstable site conditions during the site visit. Sample results from July of 2019 to May 2022 are reported in this data release. Booth, A., Fleck, J., Pellerin, B.A., Hansen, A., Etheridge, A., Foster, G.M., Graham, J.L., Bergamaschi, B.A., Carpenter, K.D., Downing, B.D., Rounds, S.A., and Saraceno, J., 2023, Field techniques for fluorescence measurements targeting dissolved organic matter, hydrocarbons, and wastewater in environmental waters: Principles and guidelines for instrument selection, operation and maintenance, quality assurance, and data reporting: U.S. Geological Survey Techniques and Methods, book 1, chap. D11, 41 p., https://doi.org/10.3133/tm1D11. Wagner, R.J., Boulger, R.W., Jr., Oblinger, C.J., and Smith, B.A., 2006, Guidelines and standard procedures for continuous water-quality monitors—Station operation, record computation, and data reporting: U.S. Geological Survey Techniques and Methods 1–D3, 51 p. + 8 attachments; accessed August 3, 2022, at https://pubs.usgs.gov/tm/2006/tm1D3/pdf/TM1D3.pdf.

This data release includes monitoring data collected by the U.S. Geological Survey (USGS) Humboldt Bay Water Quality and Salt Marsh Monitoring Project. The datasets include continuous water levels collected at a 6-minute time step collected in two study marshes (Mad River and Hookton). Surface deposition, elevation changes and carbon storage (in marsh edge environments) measured in five USGS study marshes (Mad River, Manila, Jacoby, White and Hookton). The monitoring data presented in this data release represent fundamental datasets needed to manage blue carbon stocks, assess marsh vulnerability, inform sea-level rise (SLR) adaptation planning, and build coastal resiliency to climate change in Humboldt Bay, CA Additional documentation is provided in a companion report. Curtis et al, 2022 A Summary of Water-Quality and Salt Marsh Monitoring during Water Years 2013 to 2019, Humboldt Bay, CA.

This data release includes monitoring data collected by the U.S. Geological Survey (USGS) Humboldt Bay Water Quality and Salt Marsh Monitoring Project. The datasets include continuous water levels collected at a 6-minute time step collected in two study marshes (Mad River and Hookton). Surface deposition, elevation changes and carbon storage (in marsh edge environments) measured in five USGS study marshes (Mad River, Manila, Jacoby, White and Hookton). The monitoring data presented in this data release represent fundamental datasets needed to manage blue carbon stocks, assess marsh vulnerability, inform sea-level rise (SLR) adaptation planning, and build coastal resiliency to climate change in Humboldt Bay, CA Additional documentation is provided in a companion report. Curtis et al, 2022 A Summary of Water-Quality and Salt Marsh Monitoring during Water Years 2013 to 2019, Humboldt Bay, CA.

This dataset contains measurements of water quality parameters (temperature, salinity, specific conductance, dissolved oxygen, and pH) and concentrations of dissolved organic carbon (DOC), dissolved inorganic carbon (DIC), and particulate organic carbon (POC) in canals of Jean Lafitte National Historical Park and Preserve (hereafter, the Park) during wet and dry seasons in 2022 and 2023. Four field campaigns were conducted on April 26, 2022, October 27, 2022, March 1, 2023, and August 3, 2023, covering pre-, during, and post-canal backfilling construction in the Park. Data can also be found at USGS National Water Information System (NWIS, https://waterdata.usgs.gov/nwis/sw).

The data herein report continuous field measurements and specific discrete sampling events associated with water quality and carbon consitutents – both dissolved and particulate forms. These data were coupled with atmospheric flux measurements during the 2017-18 water year to estimate the net storage of fixed carbon within the marsh on an areal basis. Direct and indirect measurement showed 47 to 59% of fixed carbon is stored on site, and most loss is through dissolved inorganic carbon (DIC) export. Comparing this with other tidal wetlands in the U.S. showed similar rates of loss, and a global meta-analysis showed that lateral loss is a proportionally larger term in coastal wetland carbon budgets, relative to other terrestrial systems.

The data herein report continuous field measurements and specific discrete sampling events associated with water quality and carbon consitutents – both dissolved and particulate forms. These data were coupled with atmospheric flux measurements during the 2017-18 water year to estimate the net storage of fixed carbon within the marsh on an areal basis. Direct and indirect measurement showed 47 to 59% of fixed carbon is stored on site, and most loss is through dissolved inorganic carbon (DIC) export. Comparing this with other tidal wetlands in the U.S. showed similar rates of loss, and a global meta-analysis showed that lateral loss is a proportionally larger term in coastal wetland carbon budgets, relative to other terrestrial systems.

This dataset provides the water content, bulk density, carbon concentrations, nitrogen concentrations, and carbon content of all fourteen cores sampled in coastal Louisiana (CRMS 0224) in October of 2019. Each sample is identified by a unique identifier that corresponds to each site by depth increment combination. The pond age range associated with each site is provided. The depth increment associated with each sample is provided.

Seawater samples were collected in Chesapeake Bay for dissolved inorganic carbon (DIC) and total alkalinity (TA) from June 2016 to July 2018. They were collected in the lower half of the Bay aboard the R/V Fay Slover in collaboration with Old Dominion University's Chesapeake Bay Program Water Quality Laboratory and the VA Dept. of Environmental Quality. In the upper half of the Bay, samples were collected aboard the R/V Kerhin in collaboration with the Maryland Department of Natural Resources' Chesapeake Bay Water Quality Monitoring Program. Additional water quality parameters from the cruises were downloaded from the Chesapeake Bay program website. Additional carbonate system parameters were then computed from DIC and TA