Abstract
Thresholds for belowground decomposition rates based on nearness to groundwater were identified on a Virginia barrier island. Negative exponential decay rates (k = 0.310–0.915 yr.−1) varied according to average distance to the freshwater free surface, with lowest decay occurring in low elevations (marsh and deeper soils of a wooded swale), and highest decay occurring at mid to high elevations (surface soils in wooded swales and all dune sites). The majority of decay rate variances were explained by mean annual depth to the freshwater free surface (r2 = 0.78). Locations with mean annual groundwater depths greater than 0.95 m were substantially less affected by fluctuations in groundwater levels (r2 = 0.09) than where groundwater was near the soil surface (r2 = 0.83). Two vegetation-based decay thresholds were identified at mean annual groundwater depths of −0.041 m and 0.538 m, separating belowground decay into three groups (low, moderate, and high decay). These groups tended to correspond to the three interior barrier island plant communities (marsh, wooded swale, and dune), but with overlap. The groundwater free surface provides a useful metric that can be used in geospatial models to predict process rates and vegetation patterns in the dynamic barrier island landscape.
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References
Brantley ST, Bisset SN, Young DR, Wolner CW, Moore LJ (2014) Barrier island morphology and sediment characteristics affect the recovery of dune building grasses following storm-induced overwash. PLoS One 9(8):e104747
Brinson MM, Lugo AE, Brown S (1981) Primary productivity, decomposition and consumer activity in freshwater wetlands. Annu Rev Ecol Syst 12:123–161
Chen H, Harmon ME, Griffiths RP, Hicks W (2000) Effects of temperature and moisture on carbon respired from decomposing woody roots. For Ecol Manag 138(1):51–64
Clark JR (1991) Management of coastal barrier biosphere reserves. Bioscience 41(5):331–336
Conn CE, Day FP Jr (1997) Root decomposition across a barrier island chronosequence: litter quality and environmental controls. Plant Soil 195:351–364
Cooper HM, Chen Q, Fletcher CH, Barbee MM (2013) Assessing vulnerability due to sea-level rise in Maui, Hawai‘i using LiDAR remote sensing and GIS. Clim Chang 116:547–563
Dasgupta S, Laplante B, Meisner C, Wheeler D, Yan J (2009) The impact of sea-level rise on developing countries: a comparative analysis. Clim Chang 93:379–388
Day FP, Conn C, Crawford E, Stevenson M (2004) Long-term effects of nitrogen fertilization on plant community structure on a coastal barrier island dune chronosequence. J Coast Res 20(3):722–730
Ehrenfeld JG (1990) Dynamics and processes of barrier island vegetation. Rev Aquat Sci 2:437–480
Fetter CW (1972) Position of the saline water interface beneath oceanic islands. Water Resour Res 8(5):1307–1315
Fetter CW (2001) Applied hydrology, 4th edn. Prentice-Hall, Upper Saddle Hill
Franke R (1982) Smooth interpolation of scattered data by local thin plate splines. Computers and Mathematics with Applications 8:273–281
Gleeson SK, Tilman T (1990) Allocation and the transient dynamics of succession on poor soils. Ecology 71(3):1144–1155
Glick P, Clough J, Polaczyk A, Couvillion B, Nunley B (2013) Potential effects of sea-level rise on coastal wetlands in southeastern Louisiana. In: Brock JC, Barras JA, Williams SJ (eds.) understanding and predicting change in the coastal ecosystems of the northern Gulf of Mexico. J Coast Res Spec Issue 63:211–233
Graziani DJ, Day FP (2015) Thresholds of change in decomposition rate along a dune/swale transect on a Virginia barrier island. J Coast Res 31(1):148–154
Guofan S, Shugart HH, Young DR (1995) Simulation of transpiration sensitivity to environmental changes for shrub (Myrica cerifera) thickets on a Virginia barrier island. Ecol Model 78:235–248
Hartley HO (1961) The modified gauss-Newton method for fitting of non-linear regression functions by least squares. Technometrics 3:269–280
Hayden BP, Dueser RD, Callahan JT, Shugart HH (1991) Long-term research at the Virginia Coast Reserve. Bioscience 41(5):310–318
Hayden BP, Santos M, Shao G, Kochel R (1995) Geomorphological controls on coastal vegetation at the Virginia Coast Reserve. Geomorphology 13:283–300
Heyel SM, Day FP (2006) Long-term residual effects of nitrogen addition on a barrier island dune ecosystem. Journal of the Torrey Botancal Society 133(2):297–303
Holm LG, Plucknett DL, Pancho JV, Herberger JP (1977) The world’s worst weeds: distribution and biology. University Press of Hawaii, Honolulu
Kirwan ML, Kirwan JL, Copenheaver CA (2007) Dynamics of an estuarine forest and its response to rising sea level. Journal of Coastal Research Volume 23(2):457–463
Leatherman SP (1988) Barrier island handbook. Coastal Publication Series, University of Maryland, College Park
Maloney MC, Preston BL (2014) A geospatial dataset for US hurricane storm surge and sea-level rise vulnerability: development and case study applications. Climate Risk Management 2:26–41
Monson RK, Lipson DL, Burns SP, Turnipseed AA, Delany AC, Williams MW, Schmidt SK (2006) Winter forest soil respiration controlled by climate and microbial community composition. Nature 439(7077):711–714
Natural Resources Conservation Service (2010) Field indicators of hydric soils in the United States, Version 7.0. Vasilas LM, Hurt GW, Noble CV (eds.) USDA, NRCS, in cooperation with the National Technical Committee for Hydric Soils
Naumann JC, Young DR, Anderson JE (2008) Leaf chlorophyll fluorescence, reflectance, and physiological response to freshwater and saltwater flooding in the evergreen shrub, Myrica cerifera. Environ Exp Bot 63(1):402–409
Neckles HA, Neill C (1994) Hydrologic control of litter decomposition in seasonally flooded prairie marshes. Hydrobiologia 286:155–165
Rietbroek R, Brunnabend SE, Kusche J, Schröter J, Dahle C (2016) Revisiting the contemporary sea-level budget on global and regional scales. Proc Natl Acad Sci 113(6):1504–1509
Rodriguez-Iturbe I (2000) Ecohydrology: a hydrologic perspective of climate-soil-vegetation dynamies. Water Resour Res 36(1):3–9
Scheffer M, Carpenter S, Foley JA, Folke C, Walker B (2001) Catastrophic shifts in ecosystems. Nature 413:591–596
Sedghi NM (2015) Blue carbon in coastal freshwater/brackish marshes on the barrier islands of Virginia: belowground carbon dynamics. Old Dominion University, Norfolk, M.S. Thesis
Sevink J (1991) Soil development in the coastal dunes and its relation to climate. Landsc Ecol 6:49–56
Sorensen LH (1974) Rate of decomposition of organic matter in soil as influenced by repeated air drying-rewetting and repeated additions of organic material. Soil Biol Biochem 6:287–292
Tebaldi C, Strauss BH, Zervas CE (2012) Modelling sea level rise impacts on storm surges along US coasts. Environ Res Lett 7(1):1–11
Tupacz EG, Day FP (1990) Decomposition of roots in a seasonally flooded swamp ecosystem. Aquat Bot 37:199–214
USACE-TEC and JALBTCX (2013) Hyperspectral imagery for Hog Island, VA, 2013. Virginia Coast Reserve Long-Term Ecological Research Project Data Publication knb-lter-vcr.229.6
Vincent G, Shahriari AR, Lucot E, Badot PM, Epron D (2006) Spatial and seasonal variations in soil respiration in a temperate deciduous forest with fluctuating water table. Soil Biol Biochem 38(9):2527–2535
VITA (2013) Virginia Base Mapping Program, 2013 satellite imagery. Retrieved February 5, 2014, from https://www.vita.virginia.gov/isp/default.aspx?id=12118
Whittecar GR, Emry JS (1992) Hydrogeology of a regressive barrier island segment, Bodie Island, North Carolina: in: Cole CA and turner K (eds.) Barrier Island Ecology of the mid-Atlantic Coast: a symposium, Natural Park Service technical report NPS/SERCAHA/NRTR-93/04, pp 189-208
Wieder RK, Lang GE (1982) A critique of the analytical methods used in examining decomposition data obtained from litter bags. Ecology 63:1636–1642
Wolner CW, Moore LJ, Young DR, Brantley ST, Bissett SN, McBride RA (2013) Ecomorphodynamic feedbacks and barrier island response to disturbance: insights from the Virginia Barrier Islands, mid-Atlantic bight, USA. Geomorphology 199:115–128
Wright JM, Chambers JC (2002) Restoring riparian meadows currently dominated by Artemisa using alternative state concepts: aboveground vegetation response. Appl Veg Sci 5:237–246
Zinnert JC, Shiflett SA, Via S, Bissett S, Dows B, Manley P, Young DR (2016) Spatial–temporal dynamics in barrier island upland vegetation: the overlooked coastal landscape. Ecosystems 19(4):685–697
Acknowledgements
This paper is based on a Master’s Thesis by Matthew Smith. The research was funded by subcontract GA11020-142301 on the University of Virginia’s NSF grant DEB-1237733. Special thanks to the staff of the Anheuser-Busch Coastal Research Center for providing logistical support.
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Smith, M.L., Day, F.P. Groundwater Thresholds for Root Decomposition and the Relation to Barrier Island Plant Communities. Wetlands 37, 851–860 (2017). https://doi.org/10.1007/s13157-017-0918-0
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DOI: https://doi.org/10.1007/s13157-017-0918-0