The supersaturation of mangrove waters leads to significant CO₂ (40 Tg C a⁻¹) and CH₄ (0.19 Tg C a⁻¹) release to the atmosphere. The rates of soil mineralization imply that the turnover time of the entire soil C_ORG pool is on the order of 25 years. This time frame is supported by empirical findings that mangrove roots decompose slowly ^[14] and that mangrove soil organic matter is composed mostly of allochthonous, highly-refractory, plant-derived material that is high in lignocellulose, and hemicellulose derived mostly from leaves ^[15] that decompose slowly ^[16]. About 58% of soil carbon is mangrove-derived, a value that comes from stable isotope signatures of mangrove soils ^[17], and about one-third of the total soil carbon pool is composed of dead roots ^[2][10] that also decompose slowly ^[14]. Assuming that 4 Tg C a⁻¹ of litter is buried and that all POC export is derived from litter, then the remaining 16 Tg a⁻¹ of litter produced must fall to the forest floor where it is presumably incorporated into detritus food webs and eventually mineralized in situ. Wood that falls to the forest floor may be eventually incorporated into the soil pool, but decomposition is very slow ^[18] and likely a minor flux, so it is not included in the mass balance; also not included are benthos and zooplankton production and chemical defenses. The total soil mineralization equates to approximately 140% of mangrove NPP. This anomaly suggests that: (1) inputs from allochthonous marine and terrestrial sources are necessary to balance the mineralization outputs (158 Tg C a⁻¹); (2) a large proportion of the soil pool and its subsequent decomposition is derived from the intertidal mudflat prior to mangrove colonization; (3) wood, algae, and fauna contribute to the soil pool; and/or (4) the subsurface soil mineralization rates and subsequent export data are overestimated. It is also conceivable that root production is underestimated given that the empirical dataset (mostly for estimates of fine roots) is small and that there are some methodological shortcomings in deriving production estimates ^[10][19].

Analysis of the origin of mangrove soil organic matter indicates that about 42% of the organic matter may be derived from external sources ^[20][17]. Measurements of radiogenic and stable isotopes in a subtropical Australian mangrove indicate that century-old sequestered carbon is still susceptible to remineralization and tidal export ^[21], supporting the idea that organic carbon deposited prior to mangrove colonization continues to be decomposed, as all mangroves colonize intertidal mudflats that have considerable amounts of soil C_ORG ^[6]. Mangrove DIC export contributes nearly 60% of DIC, and 27% of DOC discharged from the world’s tropical rivers to the coastal ocean, based on comparison with tropical riverine export values in Huang et al. ^[22]. Mangroves inhabit only 0.3% of global coastal ocean area but contribute 55% of air-sea exchange compared with the global average ^[23], 28% of DIC export, 14% of C burial, and 13% of DOC + POC export, compared to global averages in ^[24] tor the world’s coastal ocean. Mangrove ecosystems thus contribute a disproportionate share to carbon cycling in tropical seas and in the global coastal ocean.

The mass balance model is only a tool to identify the major and minor pathways of carbon flow in mangrove ecosystems and is not meant to be absolute as it does not distinguish known site-specific differences in soil type, forest composition and age, tidal exchange, bioturbation, and rates of forest productivity. As noted in the tables and figures, there are considerable variations in the mean of most measurements that are not represented in the model. Nevertheless, the model is helpful in suggesting where more research is needed, such as in more measurements of canopy GPP and respiration, preferably using the eddy covariance method, root production, estimates of DOC, CH_4, and especially DIC export, as well as more empirical measurements of subsurface DIC production as well as a clearer understanding of the contribution of groundwater derived from upland and inputs from allochthonous sources, such as the adjacent catchment and coastal zone.

Net ecosystem production (NEP), derived by subtracting all respiratory losses (ecosystem respiration, R_E = R_C + R_S + R_WATER + R_MICROALGAE) from all mangrove, algal, and phytoplankton gross primary production (GPP) is 628 g C m⁻² a⁻¹ and 54 Tg C a⁻¹ for the world’s mangroves. Phytoplankton GPP and R in mangrove tidal creeks and waterways (total area = 7208 km² assuming a forest: waterway area ratio of 12 ^[10]) averaged 1524.4 and 846.9 mg C m⁻² d^{−1 [10]}. Subsurface soil respiration was excluded from the ecosystem respiration estimate because (1) the core incubation method used to measure subsurface respiration is crude and may be an overestimate; (2) it is unclear how much porewater DIC is actually derived from groundwater; and (3) the proportional amounts of dissolved carbon derived from groundwater and from subsurface respiration is unknown.) R_E was 3558 g C m⁻¹ a⁻¹ for a global R_E of 306 Tg C a^−1, and total GPP was 4186 g C m⁻² a⁻¹ for a global GPP of 360 Tg C a⁻¹. The ratio of P_GPP/R_E averaged 1.18, indicating that mangrove ecosystems are net autotrophic.

4. Conclusions

The mangrove forest floor is unique, with cracks, fissures, extensive roots, burrows, tubes, and drainage channels, and its dynamic nature facilitates non-steady-state early diagenesis of organic matter in the soil. Rate processes and edaphic conditions (e.g., temperature, redox status, salinity) oscillate in synchrony with tidal flushing and inundation and other factors such as the extent of bioturbation and weather. Rates of soil C_ORG mineralization and belowground C_ORG stocks are high, indicating rapid accumulation and recycling of organic matter within the deep (>1 m) soil horizon. On average, carbon respiration across the surface soil-air/water interface equates to only 25% of total carbon mineralized within the entire soil horizon as most respired carbon is released in a dissolved form via advective porewater exchange and/or lateral transport and subsurface tidal pumping to adjacent tidal waters. A revised carbon budget for the world’s mangrove ecosystems indicates that subsurface respiration is the second-largest respiratory flux after canopy respiration. The amounts of dissolved carbon released to adjacent tidal waters are sufficient to cause pCO₂ oversaturation of the water column, leading to tropical coastal waters being a source of CO₂ to the atmosphere. Mangrove DIC and DOC discharge contribute disproportionately to dissolved carbon discharge from the world’s low latitude rivers to the tropical coastal ocean and contribute 55% of air-sea exchange, 28% of DIC export, 14% of C burial, and 13% of DOC + POC export from the world’s wetlands and estuaries to the coastal ocean.