
海岸海洋碳循环过程与CO2负排放
Carbon cycling in costal ocean and CO2 negative emissions
海岸海洋接受大量来自陆源的碳物质和营养盐,涉及大量以碳为中心的相互作用,是重要的碳循环海域;同时,该区域也常发育具有良好圈闭条件的储-盖系统,具有明显的CO2储集潜力。该文以海岸海洋及其下发育的沉积盆地为研究对象,综述了碳物质在海岸海洋中的循环过程、CO2通量的影响因素和海岸海洋沉积盆地的储碳机理。从“双碳”角度,重点论述了海岸海洋在促进CO2负排放方面的意义、促进海洋负碳排放的潜在途径和在沉积盆地的储碳潜力及面临的问题。海岸海洋是重要的碳汇区域之一,高效率的微生物碳泵和碳酸盐碳泵是增强海岸海洋CO2负排放的核心过程;同时,海岸海洋沉积盆地中的储-盖系统,不但提供了额外的CO2封存空间,也保障了CO2封存的安全性。未来的研究应以抑制海岸海洋中碳物质向CO2转化的进程和保障沉积储层中CO2封存的安全性为主要方向,为CO2负排放提供理论依据与技术保障。
Costal ocean receives a bunch of carbon materials and nutrients from terrestrial sources, relates a lot of carbon-involving interactions. Meanwhile, it is normal that sedimentary reservoir-cap systems with good trap conditions beneath coastal ocean, these entrapments have potentials to storage CO2. This review focuses on the coastal ocean as the research object, and introduces the carbon cycle processes in coastal ocean, their factors which could influence CO2 fluxes in the carbon cycle processes, and the potential carbon storage mechanisms of the coastal marine sedimentary basins. From the perspective of “carbon peaking and carbon neutrality”, the significance of coastal oceans for “Ocean Negative Carbon Emission (ONCE)”, its potential promotion paths, carbon storage potentials in sedimentary basins and the problems faced by coastal oceans are discussed. Overall, the costal ocean is one of the important blue carbon sink areas. In the coastal marine seawater system, improving the reaction efficiency of microbial carbon pump and carbonate carbon pump have positive significance for CO2 negative emissions; The suitable reservoir-cap systems for CO2 storage beneath coastal ocean can not only provide extra spaces, but also guarantee the safety for CO2 storage. In the future, the main research directions should be to inhibit the conversion process of carbon materials to CO2 in coastal oceans and ensure the safety of CO2 storage in sedimentary reservoirs, these could provide theoretical basis and technical guarantee for CO2 negative emissions.
carbon cycling / blue carbon sink / CO2 negative emission / coastal ocean
[1] |
IPCC. IPCC special report on carbon dioxide capture and storage[R]. Cambridge, United Kingdom and New York, NY, USA, 2005: 442.
|
[2] |
|
[3] |
|
[4] |
|
[5] |
|
[6] |
Carbon capture and storage (CCS) provides a solution toward decarbonization of the global economy. The success of this solution depends on the ability to safely and permanently store CO2 This study demonstrates for the first time the permanent disposal of CO2 as environmentally benign carbonate minerals in basaltic rocks. We find that over 95% of the CO2 injected into the CarbFix site in Iceland was mineralized to carbonate minerals in less than 2 years. This result contrasts with the common view that the immobilization of CO2 as carbonate minerals within geologic reservoirs takes several hundreds to thousands of years. Our results, therefore, demonstrate that the safe long-term storage of anthropogenic CO2 emissions through mineralization can be far faster than previously postulated. Copyright © 2016, American Association for the Advancement of Science.
|
[7] |
|
[8] |
|
[9] |
|
[10] |
|
[11] |
|
[12] |
Seasonal field observations show that the North Sea, a Northern European shelf sea, is highly efficient in pumping carbon dioxide from the atmosphere to the North Atlantic Ocean. The bottom topography–controlled stratification separates production and respiration processes in the North Sea, causing a carbon dioxide increase in the subsurface layer that is ultimately exported to the North Atlantic Ocean. Globally extrapolated, the net uptake of carbon dioxide by coastal and marginal seas is about 20% of the world ocean's uptake of anthropogenic carbon dioxide, thus enhancing substantially the open ocean carbon dioxide storage.
|
[13] |
李三忠, 刘丽军, 索艳慧, 等. 碳构造:一个地球系统科学新范式[J]. 科学通报, 2023, 68(4):309-338.
|
[14] |
|
[15] |
|
[16] |
|
[17] |
|
[18] |
|
[19] |
|
[20] |
|
[21] |
|
[22] |
姚冠荣, 高全洲. 河流碳输移与陆地侵蚀-沉积过程关系的研究进展[J]. 水科学进展, 2007, 18(1):133-139.
|
[23] |
|
[24] |
An 18-year monitoring record (1978-1995) of dissolved oxygen within a region having hypoxia (dissolved oxygen less than 2 mgl(-1)) in the bottom layer was examined to describe seasonal and annual trends. The monitoring location was near or within a well-described summer hypoxic zone whose size has been up to 20,000 km(2). The monitoring data were used to hindcast the size of the hypoxic zone for before consistent shelfwide surveys started, and to predict it for 1989, when a complete shelfwide survey was not made. The concentration of total Kjeldahl nitrogen (TKN) in surface waters and concentration of bottom water oxygen were directly related, as anticipated if organic loading from surface to bottom was from in situ processes. The TKN data were used to develop a predictive relationship that suggested there was no substantial hypoxia before the 1970s, which was before nitrate flux from the Mississippi River to the Gulf of Mexico began to rise. The peak frequency in monthly hypoxic events is two to three months after both the spring maximum in discharge and nitrate loading of the Mississippi River. These results support the conclusion that persistent, large-sized summer hypoxia is a recently-developed phenomenon that began in the 1970s or early 1980s.
|
[25] |
|
[26] |
\nFor a majority of aquatic ecosystems, respiration (R)\nexceeds autochthonous gross primary production (GPP). These systems have\nnegative net ecosystem production\n([NEP]=[GPP]–R) and\nratios of [GPP]/R of <1. This net\nheterotrophy can be sustained only if aquatic respiration is subsidized by\norganic inputs from the catchment. Such subsidies imply that organic materials\nthat escaped decomposition in the terrestrial environment must become\nsusceptible to decomposition in the linked aquatic environment.\nUsing a moderate-sized catchment in North America, the Hudson River (catchment\narea 33500 km2), evidence is presented for the magnitude\nof net heterotrophy. All approaches (CO2 gas flux;\nO2 gas flux; budget and gradient of dissolved organic C;\nand the summed components of primary production and respiration within the\necosystem) indicate that system respiration exceeds gross primary production\nby ~200 g C m-2 year-1. Highly\n14C-depleted C of ancient terrestrial origin\n(1000–5000 years old) may be an important source of labile organic\nmatter to this riverine system and support this excess respiration. The\nmechanisms by which organic matter is preserved for centuries to millennia in\nterrestrial soils and decomposed in a matter of weeks in a river connect\nmodern riverine metabolism to historical terrestrial conditions.\n
|
[27] |
|
[28] |
|
[29] |
|
[30] |
|
[31] |
|
[32] |
|
[33] |
|
[34] |
|
[35] |
\n The partial pressure of carbon dioxide (pCO\n 2\n ) in surface waters and related atmospheric exchanges were measured in nine European estuaries. Averaged fluxes over the entire estuaries are usually in the range of 0.1 to 0.5 mole of CO\n 2\n per square meter per day. For wide estuaries, net daily fluxes to the atmosphere amount to several hundred tons of carbon (up to 790 tons of carbon per day in the Scheldt estuary). European estuaries emit between 30 and 60 million tons of carbon per year to the atmosphere, representing 5 to 10% of present anthropogenic CO\n 2\n emissions for Western Europe.\n
|
[36] |
|
[37] |
Most inverse atmospheric models report considerable uptake of carbon dioxide in Europe's terrestrial biosphere. In contrast, carbon stocks in terrestrial ecosystems increase at a much smaller rate, with carbon gains in forests and grassland soils almost being offset by carbon losses from cropland and peat soils. Accounting for non–carbon dioxide carbon transfers that are not detected by the atmospheric models and for carbon dioxide fluxes bypassing the ecosystem carbon stocks considerably reduces the gap between the small carbon-stock changes and the larger carbon dioxide uptake estimated by atmospheric models. The remaining difference could be because of missing components in the stock-change approach, as well as the large uncertainty in both methods. With the use of the corrected atmosphere- and land-based estimates as a dual constraint, we estimate a net carbon sink between 135 and 205 teragrams per year in Europe's terrestrial biosphere, the equivalent of 7 to 12% of the 1995 anthropogenic carbon emissions.
|
[38] |
|
[39] |
|
[40] |
. Past characterizations of the land–ocean continuum were constructed either from a continental perspective through an analysis of watershed river basin properties (COSCATs: COastal Segmentation and related CATchments) or from an oceanic perspective, through a regionalization of the proximal and distal continental margins (LMEs: large marine ecosystems). Here, we present a global-scale coastal segmentation, composed of three consistent levels, that includes the whole aquatic continuum with its riverine, estuarine and shelf sea components. Our work delineates comprehensive ensembles by harmonizing previous segmentations and typologies in order to retain the most important physical characteristics of both the land and shelf areas. The proposed multi-scale segmentation results in a distribution of global exorheic watersheds, estuaries and continental shelf seas among 45 major zones (MARCATS: MARgins and CATchments Segmentation) and 149 sub-units (COSCATs). Geographic and hydrologic parameters such as the surface area, volume and freshwater residence time are calculated for each coastal unit as well as different hypsometric profiles. Our analysis provides detailed insights into the distributions of coastal and continental shelf areas and how they connect with incoming riverine fluxes. The segmentation is also used to re-evaluate the global estuarine CO2 flux at the air–water interface combining global and regional average emission rates derived from local studies.\n
|
[41] |
|
[42] |
|
[43] |
|
[44] |
|
[45] |
|
[46] |
. The global carbon cycle is part of the much more extensive sedimentary cycle that involves large masses of carbon in the Earth's inner and outer spheres. Studies of the carbon cycle generally followed a progression in knowledge of the natural biological, then chemical, and finally geological processes involved, culminating in a more or less integrated picture of the biogeochemical carbon cycle by the 1920s. However, knowledge of the ocean's carbon cycle behavior has only within the last few decades progressed to a stage where meaningful discussion of carbon processes on an annual to millennial time scale can take place. In geologically older and pre-industrial time, the ocean was generally a net source of CO2 emissions to the atmosphere owing to the mineralization of land-derived organic matter in addition to that produced in situ and to the process of CaCO3 precipitation. Due to rising atmospheric CO2 concentrations because of fossil fuel combustion and land use changes, the direction of the air-sea CO2 flux has reversed, leading to the ocean as a whole being a net sink of anthropogenic CO2. The present thickness of the surface ocean layer, where part of the anthropogenic CO2 emissions are stored, is estimated as of the order of a few hundred meters. The oceanic coastal zone net air-sea CO2 exchange flux has also probably changed during industrial time. Model projections indicate that in pre-industrial times, the coastal zone may have been net heterotrophic, releasing CO2 to the atmosphere from the imbalance between gross photosynthesis and total respiration. This, coupled with extensive CaCO3 precipitation in coastal zone environments, led to a net flux of CO2 out of the system. During industrial time the coastal zone ocean has tended to reverse its trophic status toward a non-steady state situation of net autotrophy, resulting in net uptake of anthropogenic CO2 and storage of carbon in the coastal ocean, despite the significant calcification that still occurs in this region. Furthermore, evidence from the inorganic carbon cycle indicates that deposition and net storage of CaCO3 in sediments exceed inflow of inorganic carbon from land and produce CO2 emissions to the atmosphere. In the shallow-water coastal zone, increase in atmospheric CO2 during the last 300 years of industrial time may have reduced the rate of calcification, and continuation of this trend is an issue of serious environmental concern in the global carbon balance.\n
|
[47] |
|
[48] |
IPCC. The physical science basis[R]. Cambridge, United Kingdom and New York, NY, USA: International Panel on Climate Change, 2013.
|
[49] |
|
[50] |
刘光鼎, 陈洁. 中国海域残留盆地油气勘探潜力分析[J]. 地球物理学进展, 2005, 20(4):881-888.
|
[51] |
|
[52] |
|
[53] |
|
[54] |
|
[55] |
The battle to reduce greenhouse gas emissions and prevent the most dangerous consequences of climate change will be waged across multiple fronts, including efforts to increase energy efficiency; efforts to deploy nonfossil fuel sources, including renewable and nuclear energy; and investment in adaptation to reduce the impacts of the climate change that will occur regardless of the actions we take. But with more than 80% of the world's energy coming from fossil fuel, winning the battle also requires capturing CO2 from large stationary sources and storing that CO2 in geologic repositories. Offshore geological repositories have received relatively little attention as potential CO2 storage sites, despite their having a number of important advantages over onshore sites, and should be considered more closely.
|
[56] |
|
[57] |
IEA. Energy technology perspectives 2020: Special report on carbon capture, utilisation and storage[R]. IEA, 2020.
|
[58] |
|
[59] |
|
/
〈 |
|
〉 |