Net primary productivity is a measure of how much energy is captured through photosynthesis and converted to plant biomass. Net primary productivity is photosynthesis minus respiration.
Used to calculate:plant growth
Varies by: ecosystem
Used | ecosystem | Reference | Location: Ecosystem (study period) |
Value | Units | Notes |
---|
* | Agricultural field / vegetable garden | Lambers et. al. 1998 - Plant Physiological Ecology | Global: Cultivated Land () | 290 | g C / m2 / year | This value is the mean net primary productivity estimate for cultivated land worldwide. |
* | Airfield | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Airport terminal | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Alley | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Apartment building | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Beach | Lichter - PRIMARY SUCCESSION AND FOREST DEVELOPMENT ONCOASTAL LAKE MICHIGAN SAND DUNES | Michigan: Beach (1996-1998) | 21.3 | g C / m2 / year | This value is the average annual rate of accumulation of carbon in living biomass (aboveground and belowground). |
Beach | Lambers et. al. 1998 - Plant Physiological Ecology | Global: Rock, ice, and sand () | 1.5 | g C / m2 / year | This value is the mean net primary productivity estimate for rock, ice, and sand worldwide. | |
* | Bike lane | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Bioswale | de Gruchy et al. 2005 Biomass, productivity, and dominance... Bruce Peninsula National Park | Bruce Peninsula National Park, Ontario, Canada: Meadow marsh (June - September 1999) | 322 | g / m2 / year | This value assumes the same net primary productivity as a freshwater marsh. |
* | Boulevard (arterial) | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Bridge | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Camp | Baker et al. 2007 Effect of consumption choices on fluxes of CNP through households | Minneapolis-St. Paul, MN: Household (Early 2000s) | 97 | g C / m2 / year | We assume the same net primary productivity as that of a lawn. This value refers to a lawn that had no management. |
* | Cemetery | Baker et al. 2007 Effect of consumption choices on fluxes of CNP through households | Minneapolis-St. Paul, MN: Household (Early 2000s) | 230 | g C / m2 / year | This value refers to the net primary productivity of a moderately fertilized lawn with clippings removed. |
* | Cistern / rain barrels | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | 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) | 17 | g / m2 / year | Total productivity |
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) | 83 | g C / m2 / year | This value refers to the total productivity. | |
* | Cogeneration plant | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Compost bin | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Computer data center | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Cottages / Mobile home | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Deep water estuary | Kirchman, David L. 2011 Processes in Microbial Ecology- Ch. 4 Microbial primary production and phototrophy | Global: deep water estuary (2011) | 125 | g C / m2 / year | |
* | Derelict structures | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Diesel power plant | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Disturbed Land | Hutchison & Henry 2010- Additive Effects of Warming and Increased Nitrogen Deposition in a Temperate Old Field: Plant Productivity and the Importance of Winter | London, Ontario, Canada: old field (2006-2008) | 707 | g / m2 / year | This value refers to aboveground productivity and root biomass. |
Disturbed Land | Mellinger & McNaughton 1975 - Structure and Function of Successional Vascular Plant Communities in Central New York | Onondaga County, New York: Old field () | 2366.76816 | g / m2 / year | This value is the average community net productivity in dry weight. We converted g/m2/day to g/m2/year in order to receive an annual value. | |
* | Eelgrass meadow | Nelson & Waaland 1997 Seasonality of eelgrass, epiphyte, and grazer biomass.... | San Juan Islands, Washington: Eelgrass meadows (July 1990 - July 1992) | 1767 | g / m2 / year | annual production |
* | Elevated train | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Estuary | Howarth et al. 2006 - Wastewater and Watershed Influences etc. | Lower Hudson River Estuary: Estuary () | 270 | g / m2 / year | Pre-European settlement estimate for gross primary productivity |
Estuary | Taylor et al. 2003 - Planktonic Carbon Cycling and Transport etc. | Haverstraw Bay ("HB"): Estuary (1996 -1998) | 121839.08 | mol C / m2 / year | This value is the annual rate of net production of dissolved inorganic carbon (mol C/year/m2). We calculated this value by taking the net production (mol C/yr), dividing it by the area of study (km2), and then converting this value to mol C/m2/year. This value is for the segment of the lower Hudson River Estuary from Haverstraw Bay to the Verrazano Narrows. | |
* | Factory | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Freshwater marsh | Jervis - Primary Production in the Freshwater Marsh Ecosystem of Troy Meadows New Jersey | Troy Meadows, New Jersey: Freshwater Marsh (1956-1966) | 1665.63 | g / m2 / year | This value is the average annual net primary productivity of four freshwater marshes |
Freshwater marsh | Mitsch 1993 Wetlands | Sedge Meadow, New York - high: Freshwater Marsh (1977) | 1078 | g / m2 / year | This value is the lowest reported net primary productivity for species Larex lacustris in a Sedge meadow in New York. | |
Freshwater marsh | de Gruchy et al. 2005 Biomass, productivity, and dominance... Bruce Peninsula National Park | Bruce Peninsula National Park, Ontario, Canada: Meadow marsh (June - September 1999) | 322 | g / m2 / year | Total productivity | |
Freshwater marsh | de Gruchy et al. 2005 Biomass, productivity, and dominance... Bruce Peninsula National Park | Bruce Peninsula National Park, Ontario, Canada: Cattail marsh (June - September 1999) | 83 | g / m2 / year | Total productivity | |
Freshwater marsh | Mitsch 1993 Wetlands | Sedge Meadow, New York - high: Freshwater Marsh (1977) | 1741 | g / m2 / year | This value is the highest reported net primary productivity for species Larex lacustris in a Sedge meadow in New York. | |
* | Fuel storage tank | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Garage | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Gas station | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Geothermal pump | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Graywater recycling | Assumed | New York City: Urban Area () | 0 | kg / m2 / yr | |
* | Greenhouse / vertical farm | Lambers et. al. 1998 - Plant Physiological Ecology | Global: Cultivated Land () | 290 | g C / m2 / year | We assume the same NPP as that of cultivated land used for agriculture. This value represents the mean net primary productivity for cultivated land worldwide. |
* | Green roof | Coffman 2007- Vegetated Roof Systems: Design, Productivity, Retention, Habitat, and Sustainability in Green Roof and Ecoroof Technology | Columbus, OH: green roof (Spring 2004) | 72 | g C / m2 / year | This value refers to extensive green roof types, which have soil substrates less than 15 cm deep. |
Green roof | Coffman 2007- Vegetated Roof Systems: Design, Productivity, Retention, Habitat, and Sustainability in Green Roof and Ecoroof Technology | Columbus, OH: green roof (Spring 2004) | 193 | g C / m2 / year | This value refers to the productivity of intensive green roofs, which have soil substrate depths greater than 30 cm deep. | |
* | Hardwood swamp | Batzer et. al. 2007 - Ecology of Freshwater and Estuarine Wetlands | South Carolina: Riverine Wetland Bottomland hardwood () | 845 | g / m2 / year | This value is the annual aboveground net primary productivity. |
Hardwood swamp | Batzer et. al. 2007 - Ecology of Freshwater and Estuarine Wetlands | Louisiana : Riverine Wetlands Bottomland hardwood () | 1374 | g / m2 / year | This value is the annual aboveground net primary productivity. | |
Hardwood swamp | Batzer et. al. 2007 - Ecology of Freshwater and Estuarine Wetlands | Kentucky: Riverine Wetlands Bottomland Hardwood () | 1334 | g / m2 / year | This value is the annual aboveground net primary productivity. | |
* | Heavy rail line | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Hemlock – northern hardwood forest | Lambers et. al. 1998 - Plant Physiological Ecology | Global: Temperate Deciduous Forest () | 540 | g C / m2 / year | This value is the mean net primary productivity estimate for Temperate Deciduous Forests worldwide. |
* | High salt marsh | Long, Mason 1983 - Saltmarsh Ecology | New York: Salt marsh () | 1790 | g / m2 / year | |
* | Highway | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Hospital | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Hotel | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Landfill | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Lawn | Falk 1980 - The Primary Productivity of Lawns in a Temperate Environment | The Smithsonian Institution, Chesapeake Bay Center for Environmental Studies, Washington D.C.: Lawn () | 1649.3 | g / m2 / year | This value was the net primary productivity of Site B which was well maintained and fertilized at a rate of 550 kg/ha. |
Lawn | Baker et al. 2007 Effect of consumption choices on fluxes of CNP through households | Minneapolis-St. Paul, MN: Household (Early 2000s) | 347 | g C / m2 / year | This is the net primary productivity of a lawn which was highly fertilized and whose clippings were removed. | |
Lawn | Baker et al. 2007 Effect of consumption choices on fluxes of CNP through households | Minneapolis-St. Paul, MN: Household (Early 2000s) | 283 | g C / m2 / year | This is the net primary productivity of a lawn which was moderately fertilized. Its clippings were left on the lawn. | |
Lawn | Falk 1980 - The Primary Productivity of Lawns in a Temperate Environment | The Smithsonian Institution, Chesapeake Bay Center for Environmental Studies, Washington D.C.: Lawn () | 1669.2 | g / m2 / year | This value is the net primary productivity of Site A which was a 10-year-old lawn that had never been irrigated or fertilized and was cut about every two weeks during the growing season. | |
Lawn | Dorney et al. 1984 Composition and structure of an urban woody plant community | Shorewood, WI: Suburbia (Spring 1980) | 2.75 | metric tons per hectare per year | ||
Lawn | Baker et al. 2007 Effect of consumption choices on fluxes of CNP through households | Minneapolis-St. Paul, MN: Household (Early 2000s) | 230 | g C / m2 / year | This is the net primary productivity of a lawn which was moderately fertilized and whose clippings were removed. | |
Lawn | Baker et al. 2007 Effect of consumption choices on fluxes of CNP through households | Minneapolis-St. Paul, MN: Household (Early 2000s) | 427 | g C / m2 / year | This is the net primary productivity of a lawn which was highly fertilized and whose clippings were left on. | |
Lawn | Baker et al. 2007 Effect of consumption choices on fluxes of CNP through households | Minneapolis-St. Paul, MN: Household (Early 2000s) | 97 | g C / m2 / year | This is the net primary productivity of a lawn that had no management. | |
* | Light rail line | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Low salt marsh | Long, Mason 1983 - Saltmarsh Ecology | New York: Salt marsh () | 1790 | g / m2 / year | |
* | Meadow | Huston 2009. The global distribution of net primary production: resolving the paradox | Global: Temperate Grasslands () | 393 | g C / m2 / year | Current estimate (not historic) |
* | Mixed use: office / residential building | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Mixed use: restaurant / office building | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Mixed use: restaurant / residential building | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Mixed use: restaurant / retail building | Assumed | New York City: Urban Area () | 0 | kg / m2 / yr | |
* | Mixed use: retail / office building | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Mixed use: retail / residential building | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Natural gas power plant | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Oak hickory forest | Lambers et. al. 1998 - Plant Physiological Ecology | Global: Temperate Deciduous Forest () | 540 | g C / m2 / year | This value is the mean net primary productivity estimate for Temperate Deciduous Forests worldwide. |
* | Office building | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Orchard | Faqi et. al. 2007 - Net primary production and nutrient cycling in an apple orchard | Loess Plateau, China: Apple Orchard () | 5.93 | short tons/ ha / year | This is the net primary productivity of qinguan apples. |
Orchard | Faqi et. al. 2007 - Net primary production and nutrient cycling in an apple orchard | Loess Plateau, China: Apple Orchard () | 3.97 | short tons/ ha / year | This is the net primary productivity of a fuji apple orchard. | |
* | Ornamental garden | Dorney et al. 1984 Composition and structure of an urban woody plant community | Shorewood, WI: Suburbia (Spring 1980) | 0.49 | kg / m2 / yr | |
Ornamental garden | Esser et al. 2000. Osnabrück Net Primary Productivity Data Set | USA: Pasture (1965) | 2600 | g / m2 / year | Total net primary productivity. Data from Ashley, D.A., et al. 1965 for irrigated and fertilized, Cynodon dactylon dominated pasture | |
Ornamental garden | Esser et al. 2000. Osnabrück Net Primary Productivity Data Set | USA (34 deg latitude/-118 deg longitude): Pasture (1966) | 2720 | g / m2 / year | Total net primary productivity. Data from Adegbola, A.R., et al. 1966, for Cynodon dactylon fertilized pasture | |
* | Parking lot | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Park savanna | Nowak, David and Crane, Daniel 2001 Carbon storage and sequestration by urban trees in the USA | United States: ecological (2001) | 120 | g C / m2 / year | |
* | Paved ball field/court | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Pedestrian bridge | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Pedestrian street / plaza | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Permeable pavers | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Photovoltaic panels | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Pier | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Pond | Lindeman 1942 Trophic-dynamic aspect of ecology | Lake Mendota, Wisconsin: Temperate lake (1930s-1940s) | 480 | g / cm2 / year | Net productivity. Original units: g-cal/cm2/year |
Pond | Westlake 1963 Comparison of Plant Productivity | Lake Erken, Sweden: Eutrophic lake (1954) | 2 | metric tons per hectare per year | annual mean productivity (dry weight); mid-point value between 1.5 - 2.5 mt/ha-year; includes diatoms | |
Pond | Lindeman 1942 Trophic-dynamic aspect of ecology | Cedar Bog Lake, Minnesota: Eutrophic lake (1930s-1940s) | 111.3 | g / cm2 / year | Net productivity. Original units: g-cal/cm2/year | |
* | Public assembly hall | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
Puddles on hardtops | NULL REFERENCE | NULL REFERENCE LOCATON: NULL ECOSYSTEM (NULL STUDY PERIOD) | None | DUMMY UNIT | ||
* | Restaurant | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Retail building | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | School or university | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Sewage treatment plant | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Shrub land | Lambers et. al. 1998 - Plant Physiological Ecology | Global: Woodland and shrubland () | 270 | g C / m2 / year | This value is the mean net primary productivity estimate for woodland and shrubland worldwide. |
* | Sidewalk | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Single family home | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Solar energy facility | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Solar heating panels | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Solid waste transfer plant | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Stadium | Assumed | New York City: Urban Area () | 0 | g / cm2 / year | |
* | Stream | Lambers et. al. 1998 - Plant Physiological Ecology | Global: Lake and stream () | 225 | g C / m2 / year | This value is the mean net primary productivity estimate for lakes and streams worldwide. |
* | Streetcar line | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Street (collector) | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Street trees | Nowak & Crane 2002- Carbon storage and sequestration by urban trees in the USA | New York City: urban area (1996-1999) | 120 | g C / m2 / year | |
Street trees | Nowak et al. 2007 New York City's Urban Forest | New York City: Urban forest (1996) | 0.21 | short tons C per acre per year | carbon sequestration rate | |
* | Subway | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Swimming pool | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Tidal energy facility | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Traffic slowed street | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Trail | Assumed | New York City: Urban Area () | 0 | g / m2 / year | |
* | Tunnel | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Utility yard | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Warehouse | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Waste energy power plant | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Water treatment plant | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Water/wastewater storage tank | Assumed | New York City: Urban Area () | 0 | g C / m2 / year | |
* | Wind farm | Assumed | New York City: Urban Area () | 0 | g C / m2 / year |