<rdf:RDF xmlns:dc="http://purl.org/dc/elements/1.1/" xmlns:dct="http://purl.org/dc/terms/" xmlns:rdf="http://www.w3.org/1999/02/22-rdf-syntax-ns#">
  <rdf:Description rdf:about="https://doi.org/10.5061/dryad.931zcrjtp">
    <dct:isReferencedBy>IMPACT4SOIL</dct:isReferencedBy>
    <dct:isReferencedBy>OpenAire</dct:isReferencedBy>
    <dct:isReferencedBy>Datacite</dct:isReferencedBy>
    <dct:license>unspecified</dct:license>
    <dct:created>2024-06-03</dct:created>
    <dct:available>2024-06-17</dct:available>
    <dc:description>unspecifiedRising atmospheric carbon dioxide levels are impacting global  temperatures, ecological systems, and human societies. Natural carbon  sequestration through the conservation of soil and native ecosystems may  slow or reduce the amount of CO2 in the atmosphere, and thus slow or  mitigate the rate of global warming. Most of the research investigating  carbon sequestration in natural systems occurs in forested ecosystems,  however rare ecosystems such as coastal plain marshes and wet-mesic sand  prairie collectively may serve as significant carbon sinks. Our objectives  were to measure and assess the importance of carbon sequestration in three  rare ecosystems (oak-pine barrens, coastal plain marsh, and wet-mesic sand  prairie) in western Lower Michigan. We measured carbon in standing  vegetation, dead organic matter, and soils within each ecosystem and  adjacent encroaching forested areas. Driven by tree carbon, total carbon  stocks in encroaching areas were greater than in intact rare ecosystems.  Soil organic carbon was greater in all intact ecosystems, though only  significantly so in coastal plain marsh.&#160; Principal components  analysis explained 72% of the variation and revealed differences between  intact ecosystems and their encroaching areas. Linear models using the  ratio of red to green light reflectance successfully predicted SOC in  intact coastal plain marsh and wet-mesic sand prairie. Our results infer  the importance of these rare ecosystems in sequestering carbon in soils  and support the need to establish federal or state management practices  for the conservation of these systems. </dc:description>
    <dc:description>unspecifiedRising atmospheric carbon dioxide levels are impacting global  temperatures, ecological systems, and human societies. Natural carbon  sequestration through the conservation of soil and native ecosystems may  slow or reduce the amount of CO2 in the atmosphere, and thus slow or  mitigate the rate of global warming. Most of the research investigating  carbon sequestration in natural systems occurs in forested ecosystems,  however rare ecosystems such as coastal plain marshes and wet-mesic sand  prairie collectively may serve as significant carbon sinks. Our objectives  were to measure and assess the importance of carbon sequestration in three  rare ecosystems (oak-pine barrens, coastal plain marsh, and wet-mesic sand  prairie) in western Lower Michigan. We measured carbon in standing  vegetation, dead organic matter, and soils within each ecosystem and  adjacent encroaching forested areas. Driven by tree carbon, total carbon  stocks in encroaching areas were greater than in intact rare ecosystems.  Soil organic carbon was greater in all intact ecosystems, though only  significantly so in coastal plain marsh.&#160; Principal components  analysis explained 72% of the variation and revealed differences between  intact ecosystems and their encroaching areas. Linear models using the  ratio of red to green light reflectance successfully predicted SOC in  intact coastal plain marsh and wet-mesic sand prairie. Our results infer  the importance of these rare ecosystems in sequestering carbon in soils  and support the need to establish federal or state management practices  for the conservation of these systems. # README: Carbon stocks in rare ecosystems  [https://doi.org/10.5061/dryad.931zcrjtp](https://doi.org/10.5061/dryad.931zcrjtp) We have submitted our site environmental data (**C.sites.env_open.xlsx**), carbon stocks (**C.data_open.xlsx**), soil bulk density and percent carbon (**SOC.calc_open.xlsx**), and all files related to spatial modeling (**C_spatialdata_(1).zip**). Descriptions **C.sites.env_open** * Date indicates the date the environmental data were collected. NA indicates the date information was not recorded and is not available * Community refers to the ecosystem in which the site was located * Type has two categorical variables, 'Buffer' which represents encroaching forests, and 'Transect' which represents intact ecosystem * Site includes the values 1 and 2, indicative of the two paired locations (intact and encroaching) used to measure carbon * Sample Code is a combination of the ecosystem type (abbreviations are CPM for coastal plain marsh, OPB for oak-pine barrens, and WMP for wet-mesic prairie) and the sample number * HumidityPer indicates the percent humidity of the air * WindSpeedMph indicates the wind speed in miles per hour * AirT indicates the air temperature in Fahrenheit * SoilpH indicates the soil pH at approximately 12.5 cm depth * SoilT indicates the soil temperature in Celsius **C.data_open** * ID is a unique identifier assigned the row in the dataset * Date indicates the date samples and data were collected to quantify carbon stocks. NA indicates the date information was not recorded and is not available * Ecosystem refers to the ecosystem in which the site was located * Type&#160;has two categorical variables, 'Encroaching' which represents encroaching forests, and 'Intact' which represents intact ecosystem * Site includes the values 1 and 2, indicative of the two paired locations (intact and encroaching) used to measure carbon * Sample Code is a combination of the ecosystem type (abbreviations are CPM for coastal plain marsh, OPB for oak-pine barrens, and WMP for wet-mesic prairie) and the sample number * TreetCha indicates the carbon measured in trees - aboveground in metric tons per hectare * DOMtCha indicates the carbon measured in dead organic matter in metric tons per hectare * HerbtCha&#160;indicates the carbon measured in the herbaceous layer in metric tons per hectare * SOCtCha&#160;indicates the carbon measured in soil organic carbon in metric tons per hectare * TotwSOCtCha&#160;indicates the total carbon measured in metric tons per hectare, or the sum of trees aboveground, DOM, herbaceous plants, and soil organic carbon. * TotwoSOCtCha&#160;indicates the total carbon measured in metric tons per hectare, or the sum of trees aboveground, DOM, and herbaceous plants. NO soil organic carbon. * Red_band1 indicates the RGB code of reflectance for red light from NAIP imagery * Green_band2 indicates the RGB code of reflectance for green light from NAIP imagery * Blue_band3&#160;indicates the RGB code of reflectance for blue light from NAIP imagery * IR_band4&#160;indicates the RGB code of reflectance for infrared light from NAIP imagery **SOC.calc_open** We collected soil samples using an auger from two subplots collected after the organic layer (leaf litter) was removed. These subsamples are denoted A and B. After these soil samples were homogenized and sieved, two more samples were collected for processing through ignition. This means that each site has four corresponding values (1A, 1B, 2A, 2B) for %organic matter and bulk density. %C Tab ---&#160; * Community indicates the ecosystem in which the site was located * Type has two categorical variables, 'Buffer' which represents encroaching forests, and 'Transect' which represents intact ecosystem * Soil site/plot/ecosystem indicates the separate samples (1A, 1B, 2A, 2B) for each site combined with the ecosystem type and site number. CPM refers to coastal plain marsh, OPB refers to oak-pine barrens, and WMP refers to wet-mesic prairie. * %OM indicates the percent organic matter lost through ignition at 500 Celsius. BulkDen Tab --- * Ecosystem includes abbreviations for coastal plain marsh (CPM), oak-pine barrens (OPB), and wet-mesic prairie (WMP). * Type includes Encroaching and Intact and encroaching to indicate site type * Bulk density was measured in four subsamples (1A, 1B, 2A, 2B) in grams per cubic centimeter **C_spatialdata_(1).zip** We used imagery circa 2016 from the National Agriculture Inventory Program (NAIP) to map soil organic carbon (SOC) based on models developed from field-collected soil and vegetation data within coastal plain marshes and wet-mesic sand prairies at Allegan State Game Area, Michigan, USA. Linear models using the red to green light reflectance ratio successfully predicted soil organic carbon within those two ecosystems. The files in this dataset include NAIP imagery of the area surrounding a coastal plain marsh and wet-mesic prairie within the Allegan State Game Area and Muskegon State Game Area. The Allegan State Game Area site was used for model development. The Muskegon State Game Area site was used for model validation. | &#8226; asga _naip2016.tif | | | :------------------- | :------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------ | | | Allegan State Game Area NAIP imagery circa 2016 | | | NAIP Imagery 2016 (acquired from Earth Explorer -[https://earthexplorer.usgs.gov/](https://earthexplorer.usgs.gov/)) | | | Location: subset of Allegan State Game Area, Michigan, USA | | | Spatial Reference NAD 1983 UTM Zone 16 North | | | Reference: National Agriculture Inventory Program. 4-band color infrared Imagery (1-m); 2012  [cited 2023 635 Sept 21]. USDA-FSA-APFO Aerial Photography Field Office, United States Department of 636 Agriculture. [https://naip-usdaonline.hub.arcgis.com/](https://naip-usdaonline.hub.arcgis.com/). | | | | | &#8226; asga _landcov.tif | | | | Allegan State Game Area land cover classification based on 2016 NAIP imagery | | | Location: subset of Allegan State Game Area, Michigan, USA | | | Raster data file (1m resolution) | | | Spatial Reference NAD 1983 UTM Zone 16 North | | | Classification Codes: | | | &#160; &#160;0 = Upland deciduous | | | &#160; &#160;1 = Open | | | &#160; &#160;2 = Water | | | &#160; &#160;3 = Impervious | | | &#160; &#160;4 = Shadow | | | &#160; &#160;5 = Coniferous | | | &#160; &#160;6 = Aspen | | | | | &#8226; asga _soc.tif | | | | Allegan State Game Area soil organic carbon | | | Soil organic carbon (t/ha) predictions in a wet-mesic prairie and coastal plain marsh at Allegan State Game Area, Michigan, USA. | | | Values predicted from 2016 NAIP imagery and soil samples collected in the field. | | | | | &#8226; msga _naip2016.tif | | | | Muskegon State Game Area NAIP imagery circa 2016 | | | NAIP Imagery 2016 (acquired from Earth Explorer - [https://earthexplorer.usgs.gov/](https://earthexplorer.usgs.gov/)) | | | Location: subset of Muskegon State Game Area, Michigan, USA | | | Spatial Reference NAD 1983 UTM Zone 16 North | | | Reference: National Agriculture Inventory Program. 4-band color infrared Imagery (1-m); 2012  [cited 2023 635 Sept 21]. USDA-FSA-APFO Aerial Photography Field Office, United States Department of 636 Agriculture. [https://naip-usdaonline.hub.arcgis.com/](https://naip-usdaonline.hub.arcgis.com/). | | | | | &#8226; msga _landcov.tif | | | | Muskegon State Game Area land cover classification based on 2016 NAIP imagery | | | Location: subset of Muskegon State Game Area, Michigan, USA | | | Raster data file (1m resolution) | | | Spatial Reference NAD 1983 UTM Zone 16 North | | | Classification Codes: | | | &#160; &#160;0 = Upland deciduous | | | &#160; &#160;1 = Open | | | &#160; &#160;2 = Water | | | &#160; &#160;3 = Impervious | | | &#160; &#160;4 = Shadow | | | &#160; &#160;5 = Coniferous | | | &#160; &#160;6 = Aspen | | | | | &#8226; msga _soc _cpm | | | | Muskegon State Game Area soil organic carbon for coastal plain marsh | | | Location: subset of Muskegon State Game Area, Michigan, USA | | | Spatial Reference NAD 1983 UTM Zone 16 North | | | Soil organic carbon (t/ha) predictions in a coastal plain marsh at Muskegon State Game Area, Michigan, USA. Values predicted from 2016 NAIP imagery and soil samples collected in the field. | | | | | &#8226; msga _soc _wmp | | | | Muskegon State Game Area soil organic carbon for wet-mesic prairie | | | Location: subset of Muskegon State Game Area, Michigan, USA | | | Spatial Reference NAD 1983 UTM Zone 16 North | | | Soil organic carbon (t/ha) in a wet-mesic prairie at Muskegon State Game Area, Michigan, USA. Values predicted from 2016 NAIP imagery and soil samples collected in the field | </dc:description>
    <dc:subject>Carbon sequestration</dc:subject>
    <dc:subject>rare ecosystems</dc:subject>
    <dc:subject>coastal plain marsh</dc:subject>
    <dc:subject>Climate change</dc:subject>
    <dc:subject>oak-pine barrens</dc:subject>
    <dc:subject>FOS: Natural sciences</dc:subject>
    <dc:subject>wet-mesic sand prairie</dc:subject>
    <dc:creator>Woller-Skar, Meg, Locher, Alexandra, Audia, Ellen, </dc:creator>
    <dc:date>2024-06-17</dc:date>
    <dct:abstract>unspecifiedRising atmospheric carbon dioxide levels are impacting global  temperatures, ecological systems, and human societies. Natural carbon  sequestration through the conservation of soil and native ecosystems may  slow or reduce the amount of CO2 in the atmosphere, and thus slow or  mitigate the rate of global warming. Most of the research investigating  carbon sequestration in natural systems occurs in forested ecosystems,  however rare ecosystems such as coastal plain marshes and wet-mesic sand  prairie collectively may serve as significant carbon sinks. Our objectives  were to measure and assess the importance of carbon sequestration in three  rare ecosystems (oak-pine barrens, coastal plain marsh, and wet-mesic sand  prairie) in western Lower Michigan. We measured carbon in standing  vegetation, dead organic matter, and soils within each ecosystem and  adjacent encroaching forested areas. Driven by tree carbon, total carbon  stocks in encroaching areas were greater than in intact rare ecosystems.  Soil organic carbon was greater in all intact ecosystems, though only  significantly so in coastal plain marsh.&#160; Principal components  analysis explained 72% of the variation and revealed differences between  intact ecosystems and their encroaching areas. Linear models using the  ratio of red to green light reflectance successfully predicted SOC in  intact coastal plain marsh and wet-mesic sand prairie. Our results infer  the importance of these rare ecosystems in sequestering carbon in soils  and support the need to establish federal or state management practices  for the conservation of these systems. </dct:abstract>
    <dct:abstract>unspecifiedRising atmospheric carbon dioxide levels are impacting global  temperatures, ecological systems, and human societies. Natural carbon  sequestration through the conservation of soil and native ecosystems may  slow or reduce the amount of CO2 in the atmosphere, and thus slow or  mitigate the rate of global warming. Most of the research investigating  carbon sequestration in natural systems occurs in forested ecosystems,  however rare ecosystems such as coastal plain marshes and wet-mesic sand  prairie collectively may serve as significant carbon sinks. Our objectives  were to measure and assess the importance of carbon sequestration in three  rare ecosystems (oak-pine barrens, coastal plain marsh, and wet-mesic sand  prairie) in western Lower Michigan. We measured carbon in standing  vegetation, dead organic matter, and soils within each ecosystem and  adjacent encroaching forested areas. Driven by tree carbon, total carbon  stocks in encroaching areas were greater than in intact rare ecosystems.  Soil organic carbon was greater in all intact ecosystems, though only  significantly so in coastal plain marsh.&#160; Principal components  analysis explained 72% of the variation and revealed differences between  intact ecosystems and their encroaching areas. Linear models using the  ratio of red to green light reflectance successfully predicted SOC in  intact coastal plain marsh and wet-mesic sand prairie. Our results infer  the importance of these rare ecosystems in sequestering carbon in soils  and support the need to establish federal or state management practices  for the conservation of these systems. # README: Carbon stocks in rare ecosystems  [https://doi.org/10.5061/dryad.931zcrjtp](https://doi.org/10.5061/dryad.931zcrjtp) We have submitted our site environmental data (**C.sites.env_open.xlsx**), carbon stocks (**C.data_open.xlsx**), soil bulk density and percent carbon (**SOC.calc_open.xlsx**), and all files related to spatial modeling (**C_spatialdata_(1).zip**). Descriptions **C.sites.env_open** * Date indicates the date the environmental data were collected. NA indicates the date information was not recorded and is not available * Community refers to the ecosystem in which the site was located * Type has two categorical variables, 'Buffer' which represents encroaching forests, and 'Transect' which represents intact ecosystem * Site includes the values 1 and 2, indicative of the two paired locations (intact and encroaching) used to measure carbon * Sample Code is a combination of the ecosystem type (abbreviations are CPM for coastal plain marsh, OPB for oak-pine barrens, and WMP for wet-mesic prairie) and the sample number * HumidityPer indicates the percent humidity of the air * WindSpeedMph indicates the wind speed in miles per hour * AirT indicates the air temperature in Fahrenheit * SoilpH indicates the soil pH at approximately 12.5 cm depth * SoilT indicates the soil temperature in Celsius **C.data_open** * ID is a unique identifier assigned the row in the dataset * Date indicates the date samples and data were collected to quantify carbon stocks. NA indicates the date information was not recorded and is not available * Ecosystem refers to the ecosystem in which the site was located * Type&#160;has two categorical variables, 'Encroaching' which represents encroaching forests, and 'Intact' which represents intact ecosystem * Site includes the values 1 and 2, indicative of the two paired locations (intact and encroaching) used to measure carbon * Sample Code is a combination of the ecosystem type (abbreviations are CPM for coastal plain marsh, OPB for oak-pine barrens, and WMP for wet-mesic prairie) and the sample number * TreetCha indicates the carbon measured in trees - aboveground in metric tons per hectare * DOMtCha indicates the carbon measured in dead organic matter in metric tons per hectare * HerbtCha&#160;indicates the carbon measured in the herbaceous layer in metric tons per hectare * SOCtCha&#160;indicates the carbon measured in soil organic carbon in metric tons per hectare * TotwSOCtCha&#160;indicates the total carbon measured in metric tons per hectare, or the sum of trees aboveground, DOM, herbaceous plants, and soil organic carbon. * TotwoSOCtCha&#160;indicates the total carbon measured in metric tons per hectare, or the sum of trees aboveground, DOM, and herbaceous plants. NO soil organic carbon. * Red_band1 indicates the RGB code of reflectance for red light from NAIP imagery * Green_band2 indicates the RGB code of reflectance for green light from NAIP imagery * Blue_band3&#160;indicates the RGB code of reflectance for blue light from NAIP imagery * IR_band4&#160;indicates the RGB code of reflectance for infrared light from NAIP imagery **SOC.calc_open** We collected soil samples using an auger from two subplots collected after the organic layer (leaf litter) was removed. These subsamples are denoted A and B. After these soil samples were homogenized and sieved, two more samples were collected for processing through ignition. This means that each site has four corresponding values (1A, 1B, 2A, 2B) for %organic matter and bulk density. %C Tab ---&#160; * Community indicates the ecosystem in which the site was located * Type has two categorical variables, 'Buffer' which represents encroaching forests, and 'Transect' which represents intact ecosystem * Soil site/plot/ecosystem indicates the separate samples (1A, 1B, 2A, 2B) for each site combined with the ecosystem type and site number. CPM refers to coastal plain marsh, OPB refers to oak-pine barrens, and WMP refers to wet-mesic prairie. * %OM indicates the percent organic matter lost through ignition at 500 Celsius. BulkDen Tab --- * Ecosystem includes abbreviations for coastal plain marsh (CPM), oak-pine barrens (OPB), and wet-mesic prairie (WMP). * Type includes Encroaching and Intact and encroaching to indicate site type * Bulk density was measured in four subsamples (1A, 1B, 2A, 2B) in grams per cubic centimeter **C_spatialdata_(1).zip** We used imagery circa 2016 from the National Agriculture Inventory Program (NAIP) to map soil organic carbon (SOC) based on models developed from field-collected soil and vegetation data within coastal plain marshes and wet-mesic sand prairies at Allegan State Game Area, Michigan, USA. Linear models using the red to green light reflectance ratio successfully predicted soil organic carbon within those two ecosystems. The files in this dataset include NAIP imagery of the area surrounding a coastal plain marsh and wet-mesic prairie within the Allegan State Game Area and Muskegon State Game Area. The Allegan State Game Area site was used for model development. The Muskegon State Game Area site was used for model validation. | &#8226; asga _naip2016.tif | | | :------------------- | :------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------ | | | Allegan State Game Area NAIP imagery circa 2016 | | | NAIP Imagery 2016 (acquired from Earth Explorer -[https://earthexplorer.usgs.gov/](https://earthexplorer.usgs.gov/)) | | | Location: subset of Allegan State Game Area, Michigan, USA | | | Spatial Reference NAD 1983 UTM Zone 16 North | | | Reference: National Agriculture Inventory Program. 4-band color infrared Imagery (1-m); 2012  [cited 2023 635 Sept 21]. USDA-FSA-APFO Aerial Photography Field Office, United States Department of 636 Agriculture. [https://naip-usdaonline.hub.arcgis.com/](https://naip-usdaonline.hub.arcgis.com/). | | | | | &#8226; asga _landcov.tif | | | | Allegan State Game Area land cover classification based on 2016 NAIP imagery | | | Location: subset of Allegan State Game Area, Michigan, USA | | | Raster data file (1m resolution) | | | Spatial Reference NAD 1983 UTM Zone 16 North | | | Classification Codes: | | | &#160; &#160;0 = Upland deciduous | | | &#160; &#160;1 = Open | | | &#160; &#160;2 = Water | | | &#160; &#160;3 = Impervious | | | &#160; &#160;4 = Shadow | | | &#160; &#160;5 = Coniferous | | | &#160; &#160;6 = Aspen | | | | | &#8226; asga _soc.tif | | | | Allegan State Game Area soil organic carbon | | | Soil organic carbon (t/ha) predictions in a wet-mesic prairie and coastal plain marsh at Allegan State Game Area, Michigan, USA. | | | Values predicted from 2016 NAIP imagery and soil samples collected in the field. | | | | | &#8226; msga _naip2016.tif | | | | Muskegon State Game Area NAIP imagery circa 2016 | | | NAIP Imagery 2016 (acquired from Earth Explorer - [https://earthexplorer.usgs.gov/](https://earthexplorer.usgs.gov/)) | | | Location: subset of Muskegon State Game Area, Michigan, USA | | | Spatial Reference NAD 1983 UTM Zone 16 North | | | Reference: National Agriculture Inventory Program. 4-band color infrared Imagery (1-m); 2012  [cited 2023 635 Sept 21]. USDA-FSA-APFO Aerial Photography Field Office, United States Department of 636 Agriculture. [https://naip-usdaonline.hub.arcgis.com/](https://naip-usdaonline.hub.arcgis.com/). | | | | | &#8226; msga _landcov.tif | | | | Muskegon State Game Area land cover classification based on 2016 NAIP imagery | | | Location: subset of Muskegon State Game Area, Michigan, USA | | | Raster data file (1m resolution) | | | Spatial Reference NAD 1983 UTM Zone 16 North | | | Classification Codes: | | | &#160; &#160;0 = Upland deciduous | | | &#160; &#160;1 = Open | | | &#160; &#160;2 = Water | | | &#160; &#160;3 = Impervious | | | &#160; &#160;4 = Shadow | | | &#160; &#160;5 = Coniferous | | | &#160; &#160;6 = Aspen | | | | | &#8226; msga _soc _cpm | | | | Muskegon State Game Area soil organic carbon for coastal plain marsh | | | Location: subset of Muskegon State Game Area, Michigan, USA | | | Spatial Reference NAD 1983 UTM Zone 16 North | | | Soil organic carbon (t/ha) predictions in a coastal plain marsh at Muskegon State Game Area, Michigan, USA. Values predicted from 2016 NAIP imagery and soil samples collected in the field. | | | | | &#8226; msga _soc _wmp | | | | Muskegon State Game Area soil organic carbon for wet-mesic prairie | | | Location: subset of Muskegon State Game Area, Michigan, USA | | | Spatial Reference NAD 1983 UTM Zone 16 North | | | Soil organic carbon (t/ha) in a wet-mesic prairie at Muskegon State Game Area, Michigan, USA. Values predicted from 2016 NAIP imagery and soil samples collected in the field | </dct:abstract>
    <dc:title>Carbon sequestration in intact rare ecosystems and their encroaching forests (Michigan, USA)</dc:title>
    <dc:identifier>10.5061/dryad.931zcrjtp</dc:identifier>
    <dc:type>dataset</dc:type>
    <dct:references>https://doi.org/10.5061/dryad.931zcrjtp</dct:references>
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