Carbon stocks and soil sequestration rates of tropical riverine wetlands

被引:104
作者
Adame, M. F. [1 ]
Santini, N. S. [2 ]
Tovilla, C. [3 ]
Vazquez-Lule, A. [4 ]
Castro, L. [5 ]
Guevara, M. [6 ]
机构
[1] Griffith Univ, Australian Rivers Inst, Nathan, Qld 4111, Australia
[2] Univ Queensland, Sch Biol Sci, Coastal Plant Lab, St Lucia, Qld 4072, Australia
[3] Colegio Frontera Sur, Tuxtla Gutierrez, Chiapas, Mexico
[4] Comis Nacl Conocimiento & Uso Biodiversidad CONAB, Mexico City, DF, Mexico
[5] Comis Nacl Areas Nat Protegidas, Chiapas, Mexico
[6] Univ Delaware, Dept Plant & Soil Sci, Newark, DE 19716 USA
关键词
MANGROVE ECOLOGY; ECOSYSTEM CARBON; NITROGEN STOCKS; FORESTS; BIOMASS; EMISSIONS; GEOMORPHOLOGY; UNCERTAINTIES; PRODUCTIVITY; TERMINOS;
D O I
10.5194/bg-12-3805-2015
中图分类号
Q14 [生态学(生物生态学)];
学科分类号
071012 ; 0713 ;
摘要
Riverine wetlands are created and transformed by geomorphological processes that determine their vegetation composition, primary production and soil accretion, all of which are likely to influence C stocks. Here, we compared ecosystem C stocks (trees, soil and downed wood) and soil N stocks of different types of riverine wetlands (marsh, peat swamp forest and mangroves) whose distribution spans from an environment dominated by river forces to an estuarine environment dominated by coastal processes. We also estimated soil C sequestration rates of mangroves on the basis of soil C accumulation. We predicted that C stocks in mangroves and peat swamps would be larger than marshes, and that C, N stocks and C sequestration rates would be larger in the upper compared to the lower estuary. Mean C stocks in mangroves and peat swamps (784.5 +/- 73.5 and 722.2 +/- 63.6 MgC ha(-1), respectively) were higher than those of marshes (336.5 +/- 38.3 MgC ha(-1)). Soil C and N stocks of mangroves were highest in the upper estuary and decreased towards the lower estuary. C stock variability within mangroves was much lower in the upper estuary (range 744-912 MgC ha(-1)) compared to the intermediate and lower estuary (range 537-1115 MgC ha(-1)) probably as a result of a highly dynamic coastline. Soil C sequestration values were 1.3 +/- 0.2 MgC ha(-1) yr(-1) and were similar across sites. Estimations of C stocks within large areas need to include spatial variability related to vegetation composition and geomorphological setting to accurately reflect variability within riverine wetlands.
引用
收藏
页码:3805 / 3818
页数:14
相关论文
共 52 条
  • [1] Selecting cost-effective areas for restoration of ecosystem services
    Adame, M. F.
    Hermoso, V.
    Perhans, K.
    Lovelock, C. E.
    Herrera-Silveira, J. A.
    [J]. CONSERVATION BIOLOGY, 2015, 29 (02) : 493 - 502
  • [2] Carbon Stocks of Tropical Coastal Wetlands within the Karstic Landscape of the Mexican Caribbean
    Adame, Maria Fernanda
    Kauffman, J. Boone
    Medina, Israel
    Gamboa, Julieta N.
    Torres, Olmo
    Caamal, Juan P.
    Reza, Miriam
    Herrera-Silveira, Jorge A.
    [J]. PLOS ONE, 2013, 8 (02):
  • [3] Sedimentation within and among mangrove forests along a gradient of geomorphological settings
    Adame, Maria Fernanda
    Neil, David
    Wright, Sara F.
    Lovelock, Catherine E.
    [J]. ESTUARINE COASTAL AND SHELF SCIENCE, 2010, 86 (01) : 21 - 30
  • [4] Carbon payments for mangrove conservation: ecosystem constraints and uncertainties of sequestration potential
    Alongi, Daniel M.
    [J]. ENVIRONMENTAL SCIENCE & POLICY, 2011, 14 (04) : 462 - 470
  • [5] BACTERIAL PRODUCTIVITY AND MICROBIAL BIOMASS IN TROPICAL MANGROVE SEDIMENTS
    ALONGI, DM
    [J]. MICROBIAL ECOLOGY, 1988, 15 (01) : 59 - 79
  • [6] Present state and future of the world's mangrove forests
    Alongi, DM
    [J]. ENVIRONMENTAL CONSERVATION, 2002, 29 (03) : 331 - 349
  • [7] Alongi DM., 2009, The Energetics of Mangrove Forests, DOI DOI 10.1007/978-1-4020-4271-3
  • [8] [Anonymous], 2003, GOOD PRACTICE GUIDAN
  • [9] [Anonymous], 2014, CO2 EMISSIONS FUEL C
  • [10] [Anonymous], 2017, R: A Language and Environment for Statistical Computing