The amount of soil organic carbon per unit area.
Used to calculate:soil organic matter
Varies by: ecosystem
Used | ecosystem | Reference | Location: Ecosystem (study period) |
Value | Units | Notes |
---|
* | Agricultural field / vegetable garden | Pouyat et al. 2002 Soil carbon pools and fluxes in urban ecosystems | Northeast, USA: Cropland () | 6 | kg / m2 | This value is the soil carbon density of Northeast croplands at 1 m depth. |
* | Airfield | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Airport terminal | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Alley | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Apartment building | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Beach | Lichter - PRIMARY SUCCESSION AND FOREST DEVELOPMENT ONCOASTAL LAKE MICHIGAN SAND DUNES | Michigan: Beach (1996-1998) | 34.7 | Mg / ha | |
* | Bike lane | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Bioswale | Colwell 2000- Characterization of Performance Predictors and Evaluation of Mowing Practices in Biofiltration Swales | WA, USA: urban area (1999-2000) | 2.4 | % (0 - 100) | |
* | Boulevard (arterial) | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Bridge | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Camp | Assumed | New York City: Mannahatta () | 0 | kg / m2 | |
* | Cemetery | Robinson & Lundholm 2012 Ecosystem services provided by urban spontaneous vegetation | Halifax Regional Municipality, Canada: Lawn (2007) | 5.4 | % (0 - 100) | We assume the same soil organic carbon biomass density as that of a lawn. |
* | Cistern / rain barrels | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Cliffs and rock outcrops | de Gruchy et al. 2005 Biomass, productivity, and dominance... Bruce Peninsula National Park | Bruce Peninsula National Park, Ontario, Canada: Carbonate open cliff (June - September 1999) | 32.33 | % (0 - 100) | |
Cliffs and rock outcrops | Yuan 2006 Soil and vegetation on cliffs of abandoned quarries | Southern China: Quarries (2003-2006) | 1.22 | % (0 - 100) | ||
Cliffs and rock outcrops | de Gruchy et al. 2005 Biomass, productivity, and dominance... Bruce Peninsula National Park | Bruce Peninsula National Park, Ontario, Canada: Carbonate treed cliff (June - September 1999) | 41.08 | % (0 - 100) | ||
* | Cogeneration plant | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Compost bin | Assumed | New York City: Urban Area () | 100 | kg / m2 | |
* | Computer data center | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Cottages / Mobile home | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Deep water estuary | Day 1979 Litter accumulation...Dismal Swamp VA | Mixed hardwood site: Hardwood swamp (1977) | 0.0029 | g / m2 | |
* | Derelict structures | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Diesel power plant | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Disturbed Land | Pouyat et al. 2002 Soil carbon pools and fluxes in urban ecosystems | Brooklyn, NY: Urban () | 5.14 | kg / m2 | This value is the carbon density of soil in urban land which is neither undisturbed nor residential. |
Disturbed Land | Robinson & Lundholm 2012 Ecosystem services provided by urban spontaneous vegetation | Halifax Regional Municipality, Canada: Spontaneous urban vegetation (2007) | 4.3 | % (0 - 100) | ||
* | Eelgrass meadow | U.S. EPA 2012 - INVENTORY OF U.S. GREENHOUSE GAS EMISSIONS AND SINKS: 1990-2010 | United States: All () | 51 | metric tons / ha | This value represents the carbon stock in aquic soils in warm temperate, most climate regions. C stocks are for the top 30 cm of the soil profile. |
* | Elevated train | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Estuary | Day 1979 Litter accumulation...Dismal Swamp VA | Mixed hardwood site: Hardwood swamp (1977) | 0.0029 | g / m2 | This value was calculated at an old dredging site. |
* | Factory | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Freshwater marsh | Jervis - Primary Production in the Freshwater Marsh Ecosystem of Troy Meadows New Jersey | Troy Meadows, New Jersey: Freshwater Marsh (1956-1966) | 49.42 | % (0 - 100) | |
Freshwater marsh | Jervis - Primary Production in the Freshwater Marsh Ecosystem of Troy Meadows New Jersey | Troy Meadows, New Jersey: Freshwater Marsh (1956-1966) | 65.14 | % (0 - 100) | ||
* | Fuel storage tank | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Garage | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Gas station | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Geothermal pump | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Graywater recycling | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Greenhouse / vertical farm | Scharenbroch 2011. A microcosm study of the common night crawler earthworm and physical, chemical and biological properties of a designed urban soil | Chicago: Greenhouse () | 8.83 | % (0 - 100) | Study done on designed urban soil (Cornell University) for greenhouses / urban rooftops. |
* | Green roof | Getter et al. 2009 Carbon sequestration potential of extensive green roofs | Mean of eight green roofs in Michigan and Maryland: green roof () | 913 | g C / m2 | This value refers to the soil organic carbon biomass density of fabricated substrate typically used on green roofs. |
* | Hardwood swamp | Schlesinger 1977 CARBON BALANCE IN TERRESTRIAL DETRITUS | USA: northern hardwood () | 68.6 | kg C / m2 | |
* | Heavy rail line | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Hemlock – northern hardwood forest | Smith et al. 2006 Methods for calculating forest ecosystem ... carbon | Northeast US: Oak-hickory forest (125 year old stand) | 53.1 | Mg / ha | |
Hemlock – northern hardwood forest | Fisher & Likens 1973 - Energy Flow in Bear Brook, New Hampshire: An Integrative Approach to Stream Ecosystem Metabolism | Bear Brook, NH: Mature hardwood forest (1968-1970) | 550 | g / m2 | ||
* | High salt marsh | Craft, Christopher 2007 Freshwater input structures soil properties, vertical accretion, and nutrient accumulation of Georgia and U.S. tidal marshes | United States: salt marsh (2007) | 240 | g C / m2 / year | used brackish, less salinity; not flooded regularly like low salt marshes |
* | Highway | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Hospital | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Hotel | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Landfill | Pouyat et al. 2002 Soil carbon pools and fluxes in urban ecosystems | Staten Island, NY: Urban () | 20.4 | kg / m2 | This value is the soil organic C density of a refuse in Queens, NY. |
Landfill | Pouyat et al. 2002 Soil carbon pools and fluxes in urban ecosystems | Queens, NY: Urban () | 13.9 | kg / m2 | This value is the soil organic C density of a refuse in Queens, NY. | |
* | Lawn | Pouyat et al. 2002 Soil carbon pools and fluxes in urban ecosystems | Baltimore, MD: Urban () | 12.2 | kg / m2 | This value represents the mean soil organic carbon density of residential grass in Baltimore, MD. |
* | Light rail line | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Low salt marsh | Craft, Christopher 2007 Freshwater input structures soil properties, vertical accretion, and nutrient accumulation of Georgia and U.S. tidal marshes | United States: salt marsh (2007) | 190 | g C / m2 / year | salt marsh |
* | Meadow | Huston 2009. The global distribution of net primary production: resolving the paradox | Global: Temperate Grasslands () | 13 | Mg / ha | Current estimate of biomass (not historic) |
* | Mixed use: office / residential building | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Mixed use: restaurant / office building | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Mixed use: restaurant / residential building | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Mixed use: restaurant / retail building | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Mixed use: retail / office building | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Mixed use: retail / residential building | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Natural gas power plant | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Oak hickory forest | Pouyat et al. 2002 Soil carbon pools and fluxes in urban ecosystems | Baltimore, MD : Forest plots () | 1.18 | mg / m2 | This value is the mean soil bulk density of forest plots in Baltimore. The data was recorded at a depth of 15 cm within circular plots with radii of 11.35 meters. |
* | Office building | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Orchard | Pouyat et al. 2002 Soil carbon pools and fluxes in urban ecosystems | Northeast and Mid-Atlantic States, US: Urban landscape () | 6 | kg / m2 | This value is the soil carbon density of Northeast croplands at 1 m depth. |
* | Ornamental garden | Pouyat et al. 2002 Soil carbon pools and fluxes in urban ecosystems | Northeast and Mid-Atlantic States, US: Urban landscape () | 15.5 | kg / m2 | This value is the carbon density of residential urban soils at 1 meter depth. |
* | Parking lot | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Park savanna | Scharenbroch & Lloyd 2006- Particulate Organic Matter and Soil Nitrogen Availability in Urban Landscapes | Moscow, ID & Pullman, WA: urban area (2002-2003) | 15.942 | kg / m2 | |
* | Paved ball field/court | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Pedestrian bridge | Assumed | New York City: Mannahatta () | 0 | kg / m2 | |
* | Pedestrian street / plaza | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Permeable pavers | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Photovoltaic panels | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Pier | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Pond | Jervis - Primary Production in the Freshwater Marsh Ecosystem of Troy Meadows New Jersey | Troy Meadows, New Jersey: Freshwater Marsh (1956-1966) | 64.39 | % (0 - 100) | |
* | Public assembly hall | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
Puddles on hardtops | NULL REFERENCE | NULL REFERENCE LOCATON: NULL ECOSYSTEM (NULL STUDY PERIOD) | None | DUMMY UNIT | ||
* | Restaurant | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Retail building | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | School or university | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Sewage treatment plant | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Shrub land | Hibbard et. al. 2005 - An Analysis of Soil Respiration across Northern Hemisphere Temperate Ecosystems | 38.43N 120.97W: Woodland/shrubland () | 4847 | g C / m2 | |
* | Sidewalk | Assumed | New York City: Mannahatta () | 0 | kg / m2 | |
* | Single family home | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Solar energy facility | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Solar heating panels | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Solid waste transfer plant | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Stadium | Assumed | New York City: Urban Area () | 0 | kg / m2 | assumes artificial turf |
* | Stream | Fisher & Likens 1973 - Energy Flow in Bear Brook, New Hampshire: An Integrative Approach to Stream Ecosystem Metabolism | Bear Brook, NH: Stream (1968-1970) | 550 | g / m2 | "stream sediments" |
* | Streetcar line | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Street (collector) | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Street trees | Scharenbroch & Lloyd 2006- Particulate Organic Matter and Soil Nitrogen Availability in Urban Landscapes | Moscow, ID & Pullman, WA: urban area (2002-2003) | 13.83 | kg / m2 | |
* | Subway | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Swimming pool | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Tidal energy facility | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Traffic slowed street | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Trail | Pouyat R. V. et al. 2006 Carbon Storage by Urban Soils in the United States | Baltimore, MD: Urban Area () | 3.3 | kg / m2 | This value represents the estimated soil organic carbon density of both impervious and barren land use. |
* | Tunnel | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Utility yard | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Warehouse | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Waste energy power plant | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Water treatment plant | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Water/wastewater storage tank | Assumed | New York City: Urban Area () | 0 | kg / m2 | |
* | Wind farm | Assumed | New York City: Urban Area () | 0 | kg / m2 |