Environmental Management

, Volume 56, Issue 4, pp 998–1008 | Cite as

Carbon Sequestration in Tidal Salt Marshes of the Northeast United States

  • Katherine Drake
  • Holly Halifax
  • Susan C. Adamowicz
  • Christopher Craft
Article

Abstract

Tidal salt marshes provide important ecological services, habitat, disturbance regulation, water quality improvement, and biodiversity, as well as accumulation and sequestration of carbon dioxide (CO2) in vegetation and soil organic matter. Different management practices may alter their capacity to provide these ecosystem services. We examined soil properties (bulk density, percent organic C, percent N), C and N pools, C sequestration and N accumulation at four marshes managed with open marsh water management (OMWM) and four marshes that were not at U.S. Fish and Wildlife National Wildlife Refuges (NWRs) on the East Coast of the United States. Soil properties (bulk density, percent organic C, percent N) exhibited no consistent differences among managed and non-OMWM marshes. Soil organic carbon pools (0–60-cm depth) also did not differ. Managed marshes contained 15.9 kg C/m2 compared to 16.2 kg C/m2 in non-OMWM marshes. Proportionately, more C (per unit volume) was stored in surface than in subsurface soils. The rate of C sequestration, based on 137Cs and 210Pb dating of soil cores, ranged from 41 to 152 g/m2/year. Because of the low emissions of CH4 from salt marshes relative to freshwater wetlands and the ability to sequester C in soil, protection and restoration of salt marshes can be a vital tool for delivering key ecosystem services, while at the same time, reducing the C footprint associated with managing these wetlands.

Keywords

Salt marsh Radiometric dating Carbon sequestration Management US National Wildlife Refuge Carbon trading 

References

  1. Anisfeld SC, Tobin MJ, Benoit G (1999) Sedimentation rates in flow-restricted and restored salt marshes in the Long Island Sound. Estuaries 22(2A):231–244CrossRefGoogle Scholar
  2. Armentano TV, Woodwell GM (1975) Sedimentation rates in a Long Island marsh determined by 210Pb dating. Limnol Oceanogr 20(3):452–456CrossRefGoogle Scholar
  3. Artigas F, Shin JY, Hobble C, Marti-Donati A, Schäfer KVR, Pechmann I (2015) Long term carbon storage potential and CO2 sink strength of a restored salt marsh in New Jersey. Agric For Meteorol 200:313–321CrossRefGoogle Scholar
  4. Barbier EB, Hacker SD, Kennedy C, Koch EW, Stier AC, Silliman BR (2011) The value of estuarine and coastal ecosystem services. Ecol Monogr 81(2):169–193CrossRefGoogle Scholar
  5. Bartlett KB, Harriss RC (1993) Review and assessment of methane emissions from wetlands. Chemosphere 26(1–4):261–330CrossRefGoogle Scholar
  6. Blake GR, Hartage KH (1986) Bulk density. In: Klute A (ed) Methods of soil analysis. Part 1. Physical and mineralogical methods. Agron Monogr 9. ASA and SSSA, Madison, pp 363–375Google Scholar
  7. Bourn WS, and Cottam C (1950) Some biological effects of ditching tidewater marshes. Research Report 19. Fish and Wildlife Service, U.S. Department of Interior, Washington, USAGoogle Scholar
  8. Bricker-Urso S, Nixon SW, Cochran JK, Hirschberg DJ, Hunt C (1989) Accretion rates and sediment accumulation in Rhode Island salt marshes. Estuaries 12(4):300–317CrossRefGoogle Scholar
  9. Bridgham SD, Megonigal JP, Keller JK, Bliss NB, Trettin C (2006) The carbon balance of north American wetlands. Wetlands 26(4):889–916CrossRefGoogle Scholar
  10. Chmura GL, Anisfeld SC, Cahoon DR, Lynch JC (2003) Global carbon sequestration in tidal, saline wetland soils. Global Biogeochem Cycles 17(4):2201–2212CrossRefGoogle Scholar
  11. Church TM, Lord CJ III, Somayajulu BLK (1981) Uranium, thorium, and lead nuclides in a Delaware salt marsh sediment. Estuar Coast Shelf Sci 13:267–275CrossRefGoogle Scholar
  12. Clark JS, Patterson WA III (1984) Pollen, Pb-210, and opaque spherules: an integrated approach to dating and sedimentation in the intertidal environment. J Sediment Petrol 54(4):1251–1265Google Scholar
  13. Craft C (2007) Freshwater input structures soil properties, vertical accretion, and nutrient accumulation of Georgia and U.S. tidal marshes. Limnol Oceanogr 52(3):1220–1230CrossRefGoogle Scholar
  14. Craft C, Megonigal P, Broome S, Stevenson J, Freese R, Cornell J, Zheng L, Sacco J (2003) The pace of ecosystem development of constructed Spartina alterniflora marshes. Ecol Appl 13(5):1417–1432CrossRefGoogle Scholar
  15. Crain CM, Gedan KB, Dionne M (2009) Tidal restrictions and mosquito ditching in New England marshes. In: Silliman BR, Grosholz ED, Bertness MD (eds) Human impacts on salt marshes a global perspective. University of California Press, Berkeley, pp 149–169Google Scholar
  16. DeLaune RD, White JR (2012) Will coastal wetlands continue to sequester carbon in response to an increase in global sea level?: a case study of the rapidly subsiding Mississippi river deltaic plain. Clim Change 110:297–314CrossRefGoogle Scholar
  17. Diaber FC (1986) Conservation of tidal marshes. Van Nostrand Reinhold Co., New YorkGoogle Scholar
  18. Duarte CM, Middelburg JJ, Caraco N (2005) Major role of marine vegetation on the oceanic carbon cycle. Biogeosciences 2:1–8CrossRefGoogle Scholar
  19. Emmett-Mattox S, Crooks S, Findsen J (2010) Wetland grasses and gases: are tidal wetlands ready for the carbon markets? Natl Wetlands Newslett 32(6):6–10Google Scholar
  20. Environmental Protection Agency (2014) Calculations and references. Clean energy. http://www.epa.gov/cleanenergy/energy-resources/refs.html. Accessed 12 Sep 2014
  21. Ferrigno F, Jobbins DM (1968) Open marsh water management. In: Proceedings of the Annual Meeting of the New Jersey Mosquito Extermination Association 55:104–115Google Scholar
  22. Ingraham MW, Foster SG (2008) The value of ecosystem services provided by the U.S. National Wildlife Refuge System in the contiguous U.S. Ecol Econ 67:608–618CrossRefGoogle Scholar
  23. James-Pirri MJ, Erwin RM, Prosser DJ (2008) US Fish and Wildlife Service (Region 5) Salt Marsh Study, 2001–2006: an assessment of hydrologic alterations on salt marsh ecosystems along the Atlantic coast. USGS Patuxent Wildlife Research Center and University of Rhode Island, Final Report to U.S. Fish and Wildlife Service, April 2008. p 427Google Scholar
  24. Kim G, Alleman LY, Church TM (2004) Accumulation records of radionuclides and trace metals in two contrasting Delaware salt marshes. Mar Chem 87:87–96CrossRefGoogle Scholar
  25. Kirwan ML, Blum LK (2011) Enhanced decomposition offsets enhanced productivity and soil carbon accumulation in coastal wetlands responding to climate change. Biogeosciences 8:987–993CrossRefGoogle Scholar
  26. Mcleod E, Chmura GL, Bouillon S, Salm R, Björk M, Duarte CM, Lovelock CE, Schlesinger WH, Silliman BR (2011) A blueprint for blue carbon: toward an improved understanding of the role of vegetated coastal habitats in sequestering CO2. Front Ecol Environ 9(10):552–560CrossRefGoogle Scholar
  27. Morris JT, Sundareshwar PV, Nietch CT, Kjerfve B, Cahoon DR (2002) Responses of coastal wetlands to rising sea level. Ecology 83(10):2869–2877CrossRefGoogle Scholar
  28. National Oceanic and Atmospheric Administration (2013) Sea level trends. Tides and currents. http://tidesandcurrents.noaa.gov/sltrends/. Accessed 7 Apr 2014
  29. Natural Resources Conservation Service (2012) Web soil survey www.websoilsurvey.nrcs.usda.gov/. Accessed 15 June 2012, verified 22 Feb 2013). NRCS, Washington
  30. Olander LP, Cooley DM, Galik CS (2012) The potential role for management of U.S. public lands in greenhouse gas mitigation and climate policy. Environ Manag 49:523–533CrossRefGoogle Scholar
  31. Orson RA, Warren RS, Niering WA (1998) Interpreting sea level rise and rates of vertical marsh accretion in a southern New England tidal salt marsh. Estuar Coast Shelf Sci 47:419–429CrossRefGoogle Scholar
  32. Pendleton L, Donato DC, Murray BC, Crooks S, Jenkins WA, Sifleet S, Craft C, Fourqurean JW, Kauffman JB, Marbà N, Megonigal P, Pidgeon E, Herr D, Gordon D, Baldera A (2012) Estimating global “blue carbon” emissions from conversion and degradation of vegetated coastal ecosystems. PLoS One 7(9):1–7CrossRefGoogle Scholar
  33. Pendleton LH, Sutton-Grier AE, Gordon DR, Murray BC, Victor BE, Griffis RB, Lechuga JAV, Giri C (2013) Considering “coastal carbon” in existing U.S. Federal statutes and policies. Coast Manag 41(5):439–456CrossRefGoogle Scholar
  34. Phillips JD (1986) Coastal submergence and marsh fringe erosion. J Coastal Res 2(4):427–436Google Scholar
  35. Poffenbarger HJ, Needelman BA, Megonigal JP (2011) Salinity influence on methane emissions from tidal marshes. Wetlands 31:831–842CrossRefGoogle Scholar
  36. Portnoy JW, Giblin AE (1997) Biogeochemical effects of seawater restoration to diked salt marshes. Ecol Appl 7(3):1054–1063CrossRefGoogle Scholar
  37. Roman CT, Peck JA, Allen JR, King JW, Appleby PG (1997) Accretion of a New England (U.S.A.) salt marsh in response to inlet migration, storms, and sea-level rise. Estuar Coast Shelf Sci 45:717–727CrossRefGoogle Scholar
  38. SAS Institute Inc. (2011) SAS/ACCESS® 9.3 Interface to Files: Reference. SAS Institute Inc, CaryGoogle Scholar
  39. Sebold KR (1992) From marsh to farm: the landscape transformation of coastal New Jersey. U.S. Department of the Interior, National Parks Service. Historic American Buildings Survey/Historic American Engineering Record, Washington. http://www.nps.gov/history/history/online_books/nj3/index.htm. Accessed 18 April 2014
  40. Silliman BR, Bertness MD (2004) Shoreline development drives invasion of Phragmites australis and the loss of plant diversity on New England salt marshes. Conserv Biol 18(5):1424–1434CrossRefGoogle Scholar
  41. Soil Conservation Service (1975) Soil survey of Suffolk County. New York. U.S. Gov. Print. Office, WashingtonGoogle Scholar
  42. Soil Conservation Service (1978) Soil survey of Atlantic County. New Jersey. U.S. Gov. Print. Office, WashingtonGoogle Scholar
  43. Soil Conservation Service (1982) Soil survey of York County. Maine. U.S. Gov. Print. Office, WashingtonGoogle Scholar
  44. Soil Conservation Service (1984) Soil survey of Essex County, Massachusetts. Southern Part. U.S. Gov. Print. Office, WashingtonGoogle Scholar
  45. Sutton-Grier AE, Moore AK, Wiley PC, Edwards PET (2014) Incorporating ecosystem services into the implementation of existing U.S. natural resource management regulations: operationalizing carbon sequestration and storage. Mar Policy 43:246–253CrossRefGoogle Scholar
  46. UNEP and CIFOR (2014) Guiding principles for delivering coastal wetland carbon projects. United Nations Environment Programme, Nairobi, Kenya and Center for International Forestry Research, Bogor, Indonesia, pp 57Google Scholar
  47. Vincent RE, Burdick DM, Dionne M (2013) Ditching and ditch-plugging in New England salt marshes: effects on hydrology, elevation, and soil characteristics. Estuar Coast 36:610–625CrossRefGoogle Scholar
  48. Wolfe RJ (1996) Effects of open marsh water management on selected tidal marsh resources: a review. J Am Mosq Control Assoc 12:701–712Google Scholar
  49. Wolfe RJ (2005) Open marsh water management: a review of system designs and installation guidelines for mosquito control and integration in wetland habitat management. In: Proceedings of the New Jersey Mosquito Control Association vol 92, pp 3–14Google Scholar

Copyright information

© Springer Science+Business Media New York 2015

Authors and Affiliations

  • Katherine Drake
    • 1
  • Holly Halifax
    • 1
    • 2
  • Susan C. Adamowicz
    • 3
  • Christopher Craft
    • 1
  1. 1.School of Public and Environmental AffairsIndiana UniversityBloomingtonUSA
  2. 2.US Government Accountability OfficeWashingtonUSA
  3. 3.Rachel Carson National Wildlife RefugeWellsUSA

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