Attribute_Accuracy_Report:
Marsh units, and water and land boundaries inherit their accuracy from accuracy of the source data, the conceptual marsh units. The vertical accuracy of the marsh unit elevation is inherited from the 1-meter ME DEM. The uncertainty in the lifespan estimates is large because of the nature of the empirical equations used and the uncertainty in the source data. For example, a 20% variation in each of the unvegetated to vegetated marsh ratio (UVVR), elevation, bulk density and sea-level rise variables, when all in favor of reducing lifespan, may result in a combined reduction of 50% in lifespan estimate.
Negative lifespan indicates the estimated lifespan is depleted and loss is imminent. Some flagged units (see description for the FLG variable) are assigned a lifespan estimate of -9999.
The marsh polygons are bound to the borders of Maine's estuarine intertidal areas that include: 1) emergent wetlands, 2) scrub-shrub areas, 3) rooted vascular aquatic beds, 4) organic unconsolidated shores, and 5) channels of open water that are narrower than 10 meters. Occasionally, marsh units are retained in this dataset even though the imagery displayed extreme change (e.g., partially or completely converted to water) from the NWI wetland delineation (e.g., marsh units 2345, 3745). In a few areas, there are no marsh units where there is visible marsh plain (e.g., northwest of marsh unit 1824), because the areas are classified in the NWI as estuarine subtidal unconsolidated shore, which is not included as salt marsh in this analysis. In a few locations, there may be areas that that are classified as unvegetated but are in fact very sparsely vegetated. A detailed on-the-ground analysis of a single site may result in a different interpretation of the wetland and marsh unit boundaries than those established through this analysis.
Horizontal_Positional_Accuracy:
Horizontal_Positional_Accuracy_Report:
Horizontal accuracy is inherited from the source dataset that delineates the marsh units, and can be considered to be +/-6 meters.
Vertical_Positional_Accuracy:
Vertical_Positional_Accuracy_Report:
Because the elevation values are averaged over delineated polygons, vertical accuracy of marsh unit elevation depends on both the horizontal accuracy of NWI dataset and the vertical accuracy of source elevation data (1-meter ME DEM). The vertical accuracy is inherited from the source elevation dataset; it is reported to be 0.98 meters. No additional accuracy assessment of the vertical accuracy has been conducted.
Source_Information:
Source_Citation:
Citation_Information:
Originator: K.V. Ackerman
Originator: Z. Defne
Originator: N.K. Ganju
Publication_Date: 2024
Title: Elevation of marsh units in Maine salt marshes
Geospatial_Data_Presentation_Form: vector digital dataset (polygon)
Series_Information:
Series_Name: data release
Issue_Identification: DOI:10.5066/P9FRGLB0
Publication_Information:
Publication_Place: Reston, VA
Publisher: U.S. Geological Survey
Other_Citation_Details:
This dataset (Elevation of marsh units in Maine salt marshes) is within the larger data release (Geospatial characterization of salt marshes in Maine). The first link below is to the elevation data and the second link is to the data release.
Online_Linkage:
Online_Linkage: https://doi.org/10.5066/P9FRGLB0
Type_of_Source_Media: digital
Source_Time_Period_of_Content:
Time_Period_Information:
Single_Date/Time:
Calendar_Date: 2024
Source_Currentness_Reference: publication date
Source_Citation_Abbreviation: mu_elev_ME.shp
Source_Contribution:
Used the marsh unit elevation (MU_ELEV) and vegetated fraction elevation (VG_ELEV) as inputs. Projection was WGS 1984 Web Mercator Auxiliary Sphere.
Source_Information:
Source_Citation:
Citation_Information:
Originator: K.V. Ackerman
Originator: Z. Defne
Originator: N.K. Ganju
Publication_Date: 2024
Title: Unvegetated to vegetated marsh ratio in Maine salt marshes
Geospatial_Data_Presentation_Form: vector digital dataset (polygon)
Series_Information:
Series_Name: data release
Issue_Identification: DOI:10.5066/P9FRGLB0
Publication_Information:
Publication_Place: Reston, VA
Publisher: U.S. Geological Survey
Other_Citation_Details:
This dataset (Unvegetated to vegetated marsh ratio in Maine salt marshes) is within the larger data release (Geospatial characterization of salt marshes in Maine). The first link below is to the UVVR data and the second link is to the data release.
Online_Linkage:
Online_Linkage: https://doi.org/10.5066/P9FRGLB0
Type_of_Source_Media: digital
Source_Time_Period_of_Content:
Time_Period_Information:
Single_Date/Time:
Calendar_Date: 2024
Source_Currentness_Reference: publication date
Source_Citation_Abbreviation: mu_UVVR_ME.shp
Source_Contribution:
Used the unvegetated to vegetated ratio (UVVR) as input. Projection was WGS 1984 Web Mercator Auxiliary Sphere.
Process_Step:
Process_Description:
This process step and subsequent process steps were performed by the same person, Zafer Defne, in ArcGIS Pro (ver.3.0.3) unless otherwise stated. For simple operations the name of the geoprocessing tool used is given in capital letters; for complex operations, the name of the geoprocessing tool used is given in capital letters and any critical parameters used are given in parentheses, separated by a semicolon, immediately after the tool name. The input and output file names are provided in [square brackets] when necessary. Units for length and area calculations are meters (m) and square meters unless otherwise stated.
a) Join the elevation (mu_elev_ME.shp) and UVVR (mu_UVVR_ME.shp) datasets to create one shapefile with both datasets in it.
b) Convert the coordinate system to the North American Datum of 1983 (NAD 1983) geographic coordinate system and add the coordinates for polygon centroids (X_POINT, Y_POINT) to the data table using ADD_GEOMETRY_ATTRIBUTES tool.
c) Export following variables to a comma separated values file [ME_mu.csv]: X_POINT, Y_POINT, FID_CMU, UVVR, ATOT_M2, AVEG_M2, mu_ELEV, vg_ELEV, FLG.
Source_Used_Citation_Abbreviation: mu_elev_ME.shp
Source_Used_Citation_Abbreviation: mu_UVVR_ME.shp
Process_Date: 2023
Source_Produced_Citation_Abbreviation: ME_mu.csv
Process_Contact:
Contact_Information:
Contact_Organization_Primary:
Contact_Organization: U.S. Geological Survey
Contact_Person: Zafer Defne
Contact_Position: Oceanographer
Contact_Address:
Address_Type: mailing and physical address
Address: 384 Woods Hole Road
City: Woods Hole
State_or_Province: MA
Postal_Code: 02543
Contact_Voice_Telephone: 508-548-8700 x2254
Contact_Facsimile_Telephone: 508-457-2310
Contact_Electronic_Mail_Address: zdefne@usgs.gov
Process_Step:
Process_Description:
The following processing steps are performed by Zafer Defne using VDatum online (VDatum ver.4.5.1) and Matlab (ver.2021b).
a) Convert marsh unit elevations from the North American Vertical Datum of 1988 (NAVD88) to Mean Tide Level (MTL) referenced elevations.
Input the ASCII file of latitude and longitude coordinates and elevation from ME dataset (ME_mu.csv) to VDatum software, and transform vertical datum from the NAVD88 to MTL. Do this for the marsh unit elevation and elevation of the vegetated part of the marsh unit to calculate mu_ELEV_MTL and vg_ELEV_MTL, respectively. Use value from the nearest Vdatum point for any point where VDatum has no data.
b) Calculate sediment budget from UVVR based on Ganju and others (2020) with SB=-0.416*log(UVVR)-1.0749, where SB is sediment budget in kilograms per square meter per year, and log() indicates natural logarithm function.
c) Calculate total sediment flux under background relative SLR (BGRND) with SF=SB*ATOT_M2, where SF is sediment flux in kilograms per year and ATOT_M2 is total surface area of marsh unit in square meters.
d) Calculate total sediment flux under global mean sea level (GMSL) scenarios (for example, GMSL03 scenario means GMSL rise of 0.3 meters). SLR reduces vegetated marsh area, therefore, causes reduction in sediment flux. The sediment flux under SLR is calculated with SF_SLR=(SB-SLR_RATE*RHO_F)*ATOT_M2, where SF_SLR is sediment flux under SLR, RHO_F is dry bulk density of future deposited sediment. RHO_F was assigned 159 kilograms per cubic meter from Morris and others (2016). SLR_RATE is the SLR rate, calculated as SLR_RATE=(RSL2100+RSL_OFFSET)/100-RSL_VLM, where RSL2100 is the relative sea level by 2100 under a global mean sea level rise scenario, RSL_OFFSET is the offset to initiate the projection at year 2000, and RSL_VLM is the relative sea level contribution from vertical land motion.
For sea level rise projections, Sweet and others (2022) SLR data within the region were used. A total of 31 points including 8 stations and 23 grid points were within the bounding box with lower left corner of (42.3539N, -71.0503W) and upper right corner of (46.0N, -66.0W).
Interpolate the SLR_RATE from 31 points over a regular grid using GRIDDATA function with natural neighbor interpolation (grid size by 51 longitudinal by 36 latitudinal points). Assign to each marsh unit the interpolated SLR_RATE value from the nearest grid point. Do this for the three scenarios considered: GMSL rise of 0.3 meters, 0.5 meters and 1.0 meters by year 2100 and calculate sediment flux for each of them.
e) Total sediment mass in the vegetated plain above MTL is calculated with TS=vg_ELEV_MTL*AVEG_M2*RHO_E, where TS is total sediment mass, AVEG_M2 is the surface area of the vegetated part of the marsh unit and RHO_E is the dry bulk density of existing marsh substrate sediment. RHO_E was assigned 373 kilograms per cubic meters from Morris and others (2016).
f) Calculate lifespan (in years) for the background relative SLR with the equation BGRND= -TS/SF. Calculate lifespan (in years) for global mean sea level rise by 0.3 meters, 0.5 meters and 1.0 meters by year 2100 scenarios with the equation GMSL= -TS/SF_SLR for each scenario (GMSL03, GMSL05, GMSL10, respectively).
g) Output Matlab data as a comma separated text file [ME_lifespan.csv].
Source_Used_Citation_Abbreviation: ME_mu.csv
Process_Date: 2023
Source_Produced_Citation_Abbreviation: ME_lifespan.csv
Process_Step:
Process_Description:
The rest of the processing steps were done by Zafer Defne, in ArcGIS Pro (ver.3.0.3) unless otherwise stated.
a) Merge lifespan calculation results file with the marsh unit features using ADD JOIN (join field: FID_CMU).
b) For marshes that are more stable, lifespan calculation sometimes results in large numbers that are far beyond the lifespan horizon of interest. Also, positive sediment budget implies unlimited lifespan. For these units, set the maximum lifespan value to 10,000 years.
c) Set lifespan values to -9999 for units with no vegetated area or with missing elevation values (FLG values that contain any of -1 or -200 values in them) so that they can be labeled as not available or excluded while plotting the data.
d) Set legend label for lifespan values less than 0 as imminent.
e) Rearrange field names and change the projection for better performance of web services with online base maps. PROJECT(Input coordinate system= NAD 1983 UTM Zone 19N; Output coordinate system=WGS 1984 Web Mercator Auxiliary Sphere; Geographic transformation= WGS 1984 (ITRF00) to NAD 1983) the feature dataset to obtain the lifespan values [mu_lifespan_ME.shp].
Source_Used_Citation_Abbreviation: ME_lifespan.csv
Process_Date: 2023
Source_Produced_Citation_Abbreviation: mu_lifespan_ME.shp