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Journal ArticleDOI

Soil greenhouse gas fluxes from tropical coastal wetlands and alternative agricultural land uses

16 Sep 2021-Biogeosciences (Copernicus GmbH)-Vol. 18, Iss: 18, pp 5085-5096
TL;DR: In this paper, the authors measured soil GHG fluxes from three natural coastal wetlands and two alternative agricultural land uses (sugarcane farming and pasture for cattle grazing) in tropical Australia.
Abstract: . Coastal wetlands are essential for regulating the global carbon budget through soil carbon sequestration and greenhouse gas (GHG – CO2 , CH4 , and N2O ) fluxes. The conversion of coastal wetlands to agricultural land alters these fluxes' magnitude and direction (uptake/release). However, the extent and drivers of change of GHG fluxes are still unknown for many tropical regions. We measured soil GHG fluxes from three natural coastal wetlands – mangroves, salt marsh, and freshwater tidal forests – and two alternative agricultural land uses – sugarcane farming and pastures for cattle grazing (ponded and dry conditions). We assessed variations throughout different climatic conditions (dry–cool, dry–hot, and wet–hot) within 2 years of measurements (2018–2020) in tropical Australia. The wet pasture had by far the highest CH4 emissions with 1231±386 mg m - 2 d - 1 , which were 200-fold higher than any other site. Dry pastures and sugarcane were the highest emitters of N2O with 55±9 mg m - 2 d - 1 (wet–hot period) and 11±3 m g m - 2 d - 1 (hot-dry period, coinciding with fertilisation), respectively. Dry pastures were also the highest emitters of CO2 with 20±1 g m - 2 d - 1 (wet–hot period). The three coastal wetlands measured had lower emissions, with salt marsh uptake of - 0.55 ± 0.23 and - 1.19 ± 0.08 g m - 2 d - 1 of N2O and CO2 , respectively, during the dry–hot period. During the sampled period, sugarcane and pastures had higher total cumulative soil GHG emissions ( CH4+N2O ) of 7142 and 56 124 CO 2-eq kg ha - 1 yr - 1 compared to coastal wetlands with 144 to 884 CO 2-eq kg ha - 1 yr - 1 (where CO2-eq is CO2 equivalent). Restoring unproductive sugarcane land or pastures (especially ponded ones) to coastal wetlands could provide significant GHG mitigation.

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Citations
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Journal ArticleDOI
TL;DR: In this article , the feasibility of achieving quantified and secure carbon removal (negative emissions) through the restoration of coastal vegetation has been evaluated, with the conclusion that costs are highly uncertain, with lower-range estimates unrealistic for wider application, and that carbon removal using coastal blue carbon restoration therefore has questionable cost-effectiveness when considered only as a climate mitigation action, either for carbon offsetting or for inclusion in Nationally Determined Contributions.
Abstract: Mangrove forests, seagrass meadows and tidal saltmarshes are vegetated coastal ecosystems that accumulate and store large quantities of carbon in their sediments. Many recent studies and reviews have favorably identified the potential for such coastal “blue carbon” ecosystems to provide a natural climate solution in two ways: by conservation, reducing the greenhouse gas emissions arising from the loss and degradation of such habitats, and by restoration, to increase carbon dioxide drawdown and its long-term storage. The focus here is on the latter, assessing the feasibility of achieving quantified and secure carbon removal (negative emissions) through the restoration of coastal vegetation. Seven issues that affect the reliability of carbon accounting for this approach are considered: high variability in carbon burial rates; errors in determining carbon burial rates; lateral carbon transport; fluxes of methane and nitrous oxide; carbonate formation and dissolution; vulnerability to future climate change; and vulnerability to non-climatic factors. Information on restoration costs is also reviewed, with the conclusion that costs are highly uncertain, with lower-range estimates unrealistic for wider application. CO2 removal using coastal blue carbon restoration therefore has questionable cost-effectiveness when considered only as a climate mitigation action, either for carbon-offsetting or for inclusion in Nationally Determined Contributions. Many important issues relating to the measurement of carbon fluxes and storage have yet to be resolved, affecting certification and resulting in potential over-crediting. The restoration of coastal blue carbon ecosystems is nevertheless highly advantageous for climate adaptation, coastal protection, food provision and biodiversity conservation. Such action can therefore be societally justified in very many circumstances, based on the multiple benefits that such habitats provide at the local scale.

20 citations

Journal ArticleDOI
TL;DR: In this paper , the authors describe the development of a blue carbon accounting model (BlueCAM) used within the Tidal Restoration of Blue Carbon Ecosystems Methodology Determination 2022 of the Emissions Reduction Fund (ERF), which is Australia's voluntary carbon market scheme.
Abstract: Restoration of coastal wetlands has the potential to deliver both climate change mitigation, called blue carbon, and adaptation benefits to coastal communities, as well as supporting biodiversity and providing additional ecosystem services. Valuing carbon sequestration may incentivize restoration projects; however, it requires development of rigorous methods for quantifying blue carbon sequestered during coastal wetland restoration. We describe the development of a blue carbon accounting model (BlueCAM) used within the Tidal Restoration of Blue Carbon Ecosystems Methodology Determination 2022 of the Emissions Reduction Fund (ERF), which is Australia's voluntary carbon market scheme. The new BlueCAM uses Australian data to estimate abatement from carbon and greenhouse gas sources and sinks arising from coastal wetland restoration (via tidal restoration) and aligns with the Intergovernmental Panel for Climate Change guidelines for national greenhouse gas inventories. BlueCAM includes carbon sequestered in soils and biomass and avoided emissions from alternative land uses. A conservative modeled approach was used to provide estimates of abatement (as opposed to on-ground measurements); and in doing so, this will reduce the costs associated with monitoring and verification for ERF projects and may increase participation in blue carbon projects by Australian landholders. BlueCAM encompasses multiple climate regions and plant communities and therefore may be useful to others outside Australia seeking to value blue carbon benefits from coastal wetland restoration.

13 citations

Journal ArticleDOI
TL;DR: In this paper , the authors measured levels of carbon (C) abatement and nitrogen removal potential of restored coastal wetlands in subtropical Queensland, Australia, and calculated C abatements of 18.5 Mg CO2−eq ha−1
Abstract: Abstract Coastal wetland restoration is an important activity to achieve greenhouse gas (GHG) reduction targets, improve water quality, and reach the Sustainable Development Goals. However, many uncertainties remain in connection with achieving, measuring, and reporting success from coastal wetland restoration. We measured levels of carbon (C) abatement and nitrogen (N) removal potential of restored coastal wetlands in subtropical Queensland, Australia. The site was originally a supratidal forest composed of Melaleuca spp. that was cleared and drained in the 1990s for sugarcane production. In 2010, tidal inundation was reinstated, and a mosaic of coastal vegetation (saltmarshes, mangroves, and supratidal forests) emerged. We measured soil GHG fluxes (CH4, N2O, CO2) and sequestration of organic C in the trees and soil to estimate the net C abatement associated with the reference, converted, and restored sites. To assess the influence of restoration on water quality improvement, we measured denitrification and soil N accumulation. We calculated C abatement of 18.5 Mg CO2−eq ha−1 year−1 when sugarcane land transitioned to supratidal forests, 11.0 Mg CO2−eq ha−1 year−1 when the land transitioned to mangroves, and 6.2 Mg CO2−eq ha−1 year−1 when the land transitioned to saltmarshes. The C abatement was due to tree growth, soil accumulation, and reduced N2O emissions due to the cessation of fertilization. Carbon abatement was still positive, even accounting for CH4 emissions, which increased in the wetlands due to flooding and N2O production due to enhanced levels of denitrification. Coastal wetland restoration in this subtropical setting effectively reduces CO2 emissions while providing additional cobenefits, notably water quality improvement.

8 citations

Journal ArticleDOI
TL;DR: In this article, a conceptual framework was developed to synthesise and visualise the fate and transport of nitrogen from the catchments to the sea from a literature review, which can be applied to other ecosystems to understand the transport and fate of N within and between catchments.

3 citations

Journal ArticleDOI
TL;DR: In this paper , the authors analyzed a regional database of >26,000 N 2 O chamber flux measurements sampled across >150 wetlands from the Prairie Pothole Region (PPR) in the Great Plains of North America.

3 citations

References
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Journal ArticleDOI
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Journal ArticleDOI
TL;DR: In this paper, the authors construct decadal budgets for methane sources and sinks between 1980 and 2010, using a combination of atmospheric measurements and results from chemical transport models, ecosystem models, climate chemistry models and inventories of anthropogenic emissions.
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1,668 citations

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TL;DR: In this article, the potential benefits of conservation, restoration and use of marine vegetated habitats for coastal protection and climate change mitigation are assessed, and the potential benefit of using these habitats in eco-engineering solutions for coast protection is discussed.
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1,239 citations

Trending Questions (1)
What are the differences in GHG emissions between mangrove soils converted into pasture and other land uses?

The paper does not provide specific information about GHG emissions from mangrove soils converted into pasture or other land uses.