2021
DOI: 10.1002/9781119639305.ch3
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Biogeochemistry of Wetland Carbon Preservation and Flux

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Cited by 18 publications
(11 citation statements)
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“…For instance, methane (CH 4 ) emission rates and processes are highly variable and still poorly documented (Rosentreter et al., 2021). The driving forces are unclear although anoxic conditions, presence (or absence) of sulfides and salinity have been identified to influence the release of CO 2 and CH 4 (Neubauer & Megonigal, 2022). Tidal pumping is another mechanism that influences the mangrove carbon budget (Maher et al., 2018; Santos et al., 2021) that may vary with hydrogeomorphic settings.…”
Section: Coastal Environmental Settings Can Help Refine Other Key Com...mentioning
confidence: 99%
“…For instance, methane (CH 4 ) emission rates and processes are highly variable and still poorly documented (Rosentreter et al., 2021). The driving forces are unclear although anoxic conditions, presence (or absence) of sulfides and salinity have been identified to influence the release of CO 2 and CH 4 (Neubauer & Megonigal, 2022). Tidal pumping is another mechanism that influences the mangrove carbon budget (Maher et al., 2018; Santos et al., 2021) that may vary with hydrogeomorphic settings.…”
Section: Coastal Environmental Settings Can Help Refine Other Key Com...mentioning
confidence: 99%
“…In addition to the terrestrial ecosystem–atmosphere exchange of C, the aquatic C export via discharge may represent another important but often overlooked component of the boreal peatland C cycle (Cole et al., 2007; Nilsson et al., 2008). Aquatic C fluxes in the form of dissolved organic C (DOC) and dissolved inorganic C (DIC; including dissolved CO 2 and CH 4 ) are strongly coupled with vegetation structure and hydrological regime (Moore, 2003; Neubauer & Megonigal, 2021) and thus subject to change following drainage (Evans et al., 2016; Nieminen et al., 2021). However, while the aquatic C loss has been integrated with terrestrial fluxes to estimate the net ecosystem carbon balance (NECB; Chapin et al., 2006) for natural mires (Koehler et al., 2011; Nilsson et al., 2008; Roulet et al., 2007), such holistic assessment of the NECB has not been conducted for boreal drained peatland forests.…”
Section: Introductionmentioning
confidence: 99%
“…The OM that is not consumed or decomposed (recalcitrant fraction) accumulates in the soil pool, contributing to the storage of blue C (Chmura et al, 2003) that can accrete vertically over time under anoxic conditions (Morris et al, 2002). For example, root growth and sediment binding dynamics drive accumulation of coastal wetland C belowground, but loss of C via decomposition can offset these gains (Cahoon et al, 2021; Neubauer & Megonigal, 2021; Spivak et al, 2019). Redox conditions are the primary driver of OM decomposition in terrestrial systems, but under low‐oxygen conditions and where tides can introduce molecular oxygen, such as in temperate and tropical coastal wetlands, it may be less important for microbial C processing and other drivers may increasingly come into play (Chapman et al, 2019).…”
Section: Introductionmentioning
confidence: 99%