» Articles » PMID: 32292646

Blue Carbon of Mexico, Carbon Stocks and Fluxes: a Systematic Review

Abstract

Mexico has more than 750,000 ha of mangroves and more than 400,000 ha of seagrasses. However, approximately 200,000 ha of mangroves and an unknown area of seagrass have been lost due to coastal development associated with urban, industrial and tourist purposes. In 2018, the approved reforms to the General Law on Climate Change (LGCC) aligned the Mexican law with the international objectives established in the 2nd Article of the Paris Agreement. This action proves Mexico's commitment to contributing to the global target of stabilizing the greenhouse gas emissions concentration in the planet. Thus, restoring and conserving mangrove and seagrass habitats could contribute to fulfilling this commitment. Therefore, as a first step in establishing a mitigation and adaptation plan against climate change with respect to conservation and restoration actions of these ecosystems, we evaluated Mexican blue carbon ecosystems through a systematic review of the carbon stock using the standardized method of Preferred Reporting Items for Systematic Reviews and Meta-Analyses (PRISMA). We used the data from 126 eligible studies for both ecosystems ( = 1220). The results indicated that information is missing at the regional level. However, the average above and below ground organic carbon stocks from mangroves in Mexico is 113.6 ± 5.5 (95% CI [99.3-118.4]) Mg C ha and 385.1 ± 22 (95% CI [344.5-431.9]) Mg C ha, respectively. The variability in the C stocks for both blue carbon ecosystems in Mexico is related to variations in climate, hydrology and geomorphology observed along the country's coasts in addition to the size and number of plots evaluated with respect to the spatial cover. The highest values for mangroves were related to humid climate conditions, although in the case of seagrasses, they were related to low levels of hydrodynamic stress. Based on the official extent of mangrove and seagrass area in Mexico, we estimate a total carbon stock of 237.7 Tg C from mangroves and 48.1 Tg C from seagrasses. However, mangroves and seagrasses are still being lost due to land use change despite Mexican laws meant to incorporate environmental compensation. Such losses are largely due to loopholes in the legal framework that dilute the laws' effectiveness and thus ability to protect the ecosystem. The estimated emissions from land use change under a conservative approach in mangroves of Mexico were approximately 24 Tg COe in the last 20 years. Therefore, the incorporation of blue carbon into the carbon market as a viable source of supplemental finance for mangrove and seagrass protection is an attractive win-win opportunity.

Citing Articles

Do restoration strategies in mangroves recover microbial diversity? A case study in the Yucatan peninsula.

Esguerra-Rodriguez D, De Leon-Lorenzana A, Teutli C, Prieto-Davo A, Garcia-Maldonado J, Herrera-Silveira J PLoS One. 2024; 19(8):e0307929.

PMID: 39150908 PMC: 11329136. DOI: 10.1371/journal.pone.0307929.


Pneumatophore CO effluxes decrease with increased salinity in mangrove forests of Yucatan, Mexico.

Salas-Rabaza J, Yanez-Espinosa L, Cejudo E, Ceron-Aguilera G, Us-Santamaria R, Andrade J Sci Rep. 2024; 14(1):18449.

PMID: 39117708 PMC: 11310504. DOI: 10.1038/s41598-024-68822-9.


Soil organic carbon stocks increased across the tide-induced salinity transect in restored mangrove region.

Zou H, Li X, Li S, Xu Z, Yu Z, Cai H Sci Rep. 2023; 13(1):19758.

PMID: 37957248 PMC: 10643433. DOI: 10.1038/s41598-023-45411-w.


Insights into coastal microbial antibiotic resistome through a meta-transcriptomic approach in Yucatan.

Guillen-Chable F, Avila Castro L, Rodriguez-Escamilla Z, Martinez-Nunez M Front Microbiol. 2022; 13:972267.

PMID: 36325016 PMC: 9618888. DOI: 10.3389/fmicb.2022.972267.


Tourists perceptions of Caribbean islands facing environmental threats before the COVID-19 health crisis: Holbox Island and Archipelago of Bocas del Toro.

Rubio-Cisneros N, Montero-Munoz J, Rubio-Cisneros I, Morales-Ojeda S, Pech M, Ruiz-Ayma G PLoS One. 2022; 17(3):e0262014.

PMID: 35263328 PMC: 8906595. DOI: 10.1371/journal.pone.0262014.


References
1.
Schile L, Kauffman J, Crooks S, Fourqurean J, Glavan J, Megonigal J . Limits on carbon sequestration in arid blue carbon ecosystems. Ecol Appl. 2016; 27(3):859-874. DOI: 10.1002/eap.1489. View

2.
Moher D, Liberati A, Tetzlaff J, Altman D . Preferred reporting items for systematic reviews and meta-analyses: the PRISMA statement. Ann Intern Med. 2009; 151(4):264-9, W64. DOI: 10.7326/0003-4819-151-4-200908180-00135. View

3.
Adame M, Kauffman J, Medina I, Gamboa J, Torres O, Caamal J . Carbon stocks of tropical coastal wetlands within the karstic landscape of the Mexican Caribbean. PLoS One. 2013; 8(2):e56569. PMC: 3572964. DOI: 10.1371/journal.pone.0056569. View

4.
Medina-Gomez I, Madden C, Herrera-Silveira J, Kjerfve B . Response of Thalassia Testudinum Morphometry and Distribution to Environmental Drivers in a Pristine Tropical Lagoon. PLoS One. 2016; 11(10):e0164014. PMC: 5063390. DOI: 10.1371/journal.pone.0164014. View

5.
Thorhaug A, Poulos H, Lopez-Portillo J, Ku T, Berlyn G . Seagrass blue carbon dynamics in the Gulf of Mexico: Stocks, losses from anthropogenic disturbance, and gains through seagrass restoration. Sci Total Environ. 2017; 605-606:626-636. DOI: 10.1016/j.scitotenv.2017.06.189. View