三峡库区河流水体碳变化驱动力分析

程学军, 付重庆, 肖潇, 张双印, 徐坚, 郑航, 廖茂昕

raybet体育在线 院报 ›› 2024, Vol. 41 ›› Issue (12) : 66-72.

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raybet体育在线 院报 ›› 2024, Vol. 41 ›› Issue (12) : 66-72. DOI: 10.11988/ckyyb.20230911
水土保持与生态修复

三峡库区河流水体碳变化驱动力分析

作者信息 +

Drivers for Carbon Variation of River in Three Gorges Reservoir Area

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文章历史 +

摘要

为探究流域景观特征对河流碳循环过程的影响,综合运用景观指数法、冗余分析(RDA)法和Pearson相关性分析法,分析长江三峡库区段景观因子对河流碳循环的影响。 结果表明: 长江三峡库区段土地利用和景观格局对水体溶解性碳浓度和水-气界面CO2、CH4通量影响最大的缓冲区尺度为1 500 m;1 500 m缓冲区内影响水体溶解性碳的关键变量有建筑用地和林地,影响水-气界面CO2和CH4通量的关键变量有建筑用地、林地、草地、耕地、裸地、香农多样性指数(SHDI)和斑块丰富度(PRD)。

Abstract

Understanding the impact of land use and landscape patterns on river carbon cycling is crucial for improving the watershed environment. This study utilized the landscape index method, redundancy analysis (RDA), and Pearson correlation analysis to analyze the effects of landscape factors on river carbon cycling in the Three Gorges Reservoir area. The findings reveal that: 1) Within a buffer zone scale of 1 500 m, the land use and landscape patterns have a substantial impact on the concentration of dissolved carbon in water and the fluxes of CO2 and CH4 at the water-air interface. 2) The dissolved carbon within the 1 500 m buffer zone is influenced by several key variables, including built-up land, and forest land. For CO2 and CH4 fluxes at the water-air interface, influential variables include built-up land, forest land, grassland, arable land, bare land, Shannon’s diversity index (SHDI), and patch richness density (PRD).

关键词

土地利用 / 景观指数 / 温室气体 / 溶解性无机碳 / 溶解性有机碳 / 缓冲区

Key words

land use / landscape index / greenhouse gases / dissolved inorganic carbon(DIC) / dissolved organic carbon(DOC) / buffer zones

引用本文

导出引用
程学军, 付重庆, 肖潇, . 三峡库区河流水体碳变化驱动力分析[J]. raybet体育在线 院报. 2024, 41(12): 66-72 https://doi.org/10.11988/ckyyb.20230911
CHENG Xue-jun, FU Chong-qing, XIAO Xiao, et al. Drivers for Carbon Variation of River in Three Gorges Reservoir Area[J]. Journal of Yangtze River Scientific Research Institute. 2024, 41(12): 66-72 https://doi.org/10.11988/ckyyb.20230911
中图分类号: X522 (河流)   

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摘要
碳中和现已成为全球共识。为实现碳中和目标,除了发展新能源降低碳排放外,提升固碳增汇能力是其重要途径。碳汇可分为海洋碳汇和陆地碳汇两大类。海洋碳汇包括沿海生态碳汇、海水生态碳汇和人工海洋碳汇。其中,沿海生态碳汇主要由海岸植被固碳效应和沿海沉积物负载形成,海水生态碳汇主要由海洋碳泵效应形成,这两种碳汇与季风洋流条件、陆源有机物输入、海岸地理条件和人为活动直接相关,人工海洋碳汇的可行性需要综合考虑对海洋生态的影响。陆地碳汇包括陆地植被碳汇、自然地质碳汇和人工地质碳汇。其中,陆地植被碳汇是通过森林植被、草地植被以及湿地植被等植物的光合作用实现,受气温与降水、大气成分、土地利用变化以及自然干扰等因素的影响。自然地质碳汇主要由土壤碳汇和岩石风化碳汇组成,土壤碳汇受区域植被条件、气候条件和土壤利用等因素影响,而碳酸盐岩和硅酸盐岩风化作用吸收大气CO<sub>2</sub>的岩石风化碳汇主要受气温、降水、岩石类型、水文条件以及人类活动的影响。人工地质碳汇是将捕集后的CO<sub>2</sub>注入地下指定区域进行长期封存形成,其封存能力受地质构造、储盖条件、地热、地层水动力、油气潜力和盆地勘探开发程度等因素的影响。从气候环境、自然资源和社会经济等多种措施有机结合实现固碳增汇,是未来实现碳中和的有效途径。
(YANG Wei-dong, ZENG Lian-bo, LI Xiang. Advances in Research of Carbon Sinks and Their Influencing Factors Evaluation[J]. Advances in Earth Science, 2023, 38(2): 151-167.) (in Chinese)

Carbon neutrality has become a topic of global consensus. To achieve carbon neutrality, it is also important to enhance carbon sequestration and sink capabilities, apart from the development of new energy to minimize carbon emissions. Carbon sinks can be divided into marine and terrestrial types. The marine carbon sink is mainly composed of three parts: the coastal ecological carbon sink mainly formed by the carbon sequestration effect of coastal vegetation and coastal sediment load, and the marine ecological carbon sink mainly formed by dissolution and microbial pumps in the ocean. Both are directly related to monsoon oceanic current conditions, terrestrial organic inputs, coastal geographical conditions, and human activity. The feasibility of an artificial oceanic carbon sink depends on its impact on marine ecology. In terrestrial carbon sinks, vegetation carbon sinks are formed by organic carbon generated by the photosynthesis of terrestrial plants, including forest, grassland, and wetland vegetation. The influencing factors include temperature and precipitation, atmospheric composition, land use and its changes, and natural disturbance effects. Natural geological carbon sinks mostly consist of soil and karst carbon sinks. Soil carbon sinks are affected by regional vegetation, climatic conditions, soil utilization, and other factors. Karst carbon sinks are mainly produced by weathering between carbonate and silicate rocks absorbing atmospheric CO2, which is affected by temperature, precipitation, rock type, hydrological conditions, and human activity. An artificial geological carbon sink was formed because the captured CO2 was injected into the designated area underground for storage. The storage capacity depends on the evaluation of geological characteristics, reservoir conditions, oil distribution, and production. For the future, it is necessary to act decisively in climatic, natural resources, the social economy, and other aspects to fix carbon, enhance carbon sequestration, and achieve carbon neutrality.

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基金

中央级公益性科研院所基本科研业务费项目(CKSF2023296/KJ)
湖南省重大水利科技项目(XSKJ2022068-12)
2022年度知识创新专项基础研究项目(2022010801010238)

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