Wetland carbon storage controlled by millennial-scale variation in relative sea-level rise

Coastal wetlands (mangrove, tidal marsh and seagrass) sustain the highest rates of carbon sequestration per unit area of all natural systems1,2, primarily because of their comparatively high productivity and preservation of organic carbon within sedimentary substrates3. Climate change and associated relative sea-level rise (RSLR) have been proposed to increase the rate of organic-carbon burial in coastal wetlands in the first half of the twenty-first century4, but these carbon–climate feedback effects have been modelled to diminish over time as wetlands are increasingly submerged and carbon stores become compromised by erosion4,5. Here we show that tidal marshes on coastlines that experienced rapid RSLR over the past few millennia (in the late Holocene, from about 4,200 years ago to the present) have on average 1.7 to 3.7 times higher soil carbon concentrations within 20 centimetres of the surface than those subject to a long period of sea-level stability. This disparity increases with depth, with soil carbon concentrations reduced by a factor of 4.9 to 9.1 at depths of 50 to 100 centimetres. We analyse the response of a wetland exposed to recent rapid RSLR following subsidence associated with pillar collapse in an underlying mine and demonstrate that the gain in carbon accumulation and elevation is proportional to the accommodation space (that is, the space available for mineral and organic material accumulation) created by RSLR. Our results suggest that coastal wetlands characteristic of tectonically stable coastlines have lower carbon storage owing to a lack of accommodation space and that carbon sequestration increases according to the vertical and lateral accommodation space6 created by RSLR. Such wetlands will provide long-term mitigating feedback effects that are relevant to global climate–carbon modelling.Wetlands exposed to rapid sea-level rise over the late Holocene contain more soil carbon than those that experienced a long period of sea-level stability.

[1]  P. V. Sundareshwar,et al.  RESPONSES OF COASTAL WETLANDS TO RISING SEA LEVEL , 2002 .

[2]  Robert J. Orth,et al.  The Charisma of Coastal Ecosystems: Addressing the Imbalance , 2008 .

[3]  Alfred C. Redfield,et al.  Development of a New England Salt Marsh , 1972 .

[4]  Nicole Dix,et al.  Accuracy and Precision of Tidal Wetland Soil Carbon Mapping in the Conterminous United States , 2018, Scientific Reports.

[5]  B. Jones,et al.  Holocene sea-level change on the southeast coast of Australia: a review , 2007 .

[6]  Neil Saintilan,et al.  Seventy years of continuous encroachment substantially increases ‘blue carbon’ capacity as mangroves replace intertidal salt marshes , 2016, Global change biology.

[7]  I. Shennan,et al.  Holocene land‐ and sea‐level changes in Great Britain , 2002 .

[8]  A. Ellison,et al.  A World Without Mangroves? , 2007, Science.

[9]  Neil Saintilan,et al.  How mangrove forests adjust to rising sea level. , 2014, The New phytologist.

[10]  Mangrove-saltmarsh dynamics on a bay-head delta in the Hawkesbury River estuary, New South Wales, Australia , 1999 .

[11]  R. Delaune,et al.  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 , 2011, Climatic Change.

[12]  John P. Smol,et al.  Tracking Environmental Change Using Lake Sediments: Data Handling and Numerical Techniques , 2001 .

[13]  M. Kirwan,et al.  Tidal wetland stability in the face of human impacts and sea-level rise , 2013, Nature.

[14]  W. Peltier,et al.  Global Changes in Postglacial Sea Level: A Numerical Calculation , 1978, Quaternary Research.

[15]  Dan Laffoley,et al.  Mitigating climate change through restoration and management of coastal wetlands and near-shore marine ecosystems : challenges and opportunities , 2011 .

[16]  Jessica Gurevitch,et al.  Design and Analysis of Ecological Experiments , 1993 .

[17]  D. Cahoon,et al.  Global carbon sequestration in tidal, saline wetland soils , 2003 .

[18]  Carlos M. Duarte,et al.  A blueprint for blue carbon: toward an improved understanding of the role of vegetated coastal habitats in sequestering CO2 , 2011 .

[19]  Shing Yip Lee,et al.  Updated estimates of carbon accumulation rates in coastal marsh sediments , 2014 .

[20]  Simon M. Mudd,et al.  Response of salt-marsh carbon accumulation to climate change , 2012, Nature.

[21]  John Robert Lawrence Allen,et al.  Morphodynamics of Holocene salt marshes: a review sketch from the Atlantic and Southern North Sea coasts of Europe , 2000 .

[22]  M. Kanninen,et al.  Mangroves among the most carbon-rich forests in the tropics , 2011 .

[23]  B. Jones,et al.  Reconstructing recent sedimentation in two urbanised coastal lagoons (NSW, Australia) using radioisotopes and geochemistry , 2011 .

[24]  N. Pontee Defining coastal squeeze: A discussion , 2013 .

[25]  Glenn R. Guntenspergen,et al.  Influence of tidal range on the stability of coastal marshland , 2010 .

[26]  K. Lambeck,et al.  Late Pleistocene and Holocene sea-level change along the Australian coast , 1990 .

[27]  J. Pethick,et al.  Long-term Accretion Rates on Tidal Salt Marshes , 1981 .

[28]  E. D. Seneca,et al.  Loss on ignition and kjeldahl digestion for estimating organic carbon and total nitrogen in estuarine marsh soils: Calibration with dry combustion , 1991 .

[29]  R. Nicholls,et al.  Future response of global coastal wetlands to sea-level rise , 2018, Nature.

[30]  C. Woodroffe,et al.  Development of widespread mangrove swamps in mid-Holocene times in northern Australia , 1985, Nature.

[31]  C. Woodroffe,et al.  Quaternary Sea-Level Changes: A Global Perspective , 2014 .

[32]  D. Cahoon,et al.  Elevated CO2 stimulates marsh elevation gain, counterbalancing sea-level rise , 2009, Proceedings of the National Academy of Sciences.

[33]  Ana Ivelisse Avilés,et al.  Linear Mixed Models for Longitudinal Data , 2001, Technometrics.

[34]  N. Saintilan,et al.  Mangrove-saltmarsh dynamics on a bay-head delta in the Hawkesbury River estuary, New South Wales, Australia , 1999, Hydrobiologia.

[35]  D. Cahoon,et al.  The vulnerability of Indo-Pacific mangrove forests to sea-level rise , 2015, Nature.

[37]  Jack J. Middelburg,et al.  Major role of marine vegetation on the oceanic carbon cycle , 2004 .