河流-河口-近海连续体有机碳时空分布特征:以瓯江为例

申思远, 陆莎莎, 李中乔, 郑军, 王道岭

海洋学研究 ›› 2026, Vol. 44 ›› Issue (2) : 103-112.

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海洋学研究 ›› 2026, Vol. 44 ›› Issue (2) : 103-112. DOI: 10.3969/j.issn.1001-909X.2026.02.011
研究报道

河流-河口-近海连续体有机碳时空分布特征:以瓯江为例

作者信息 +

Spatial and temporal distribution characteristics of organic carbon in the river-estuary-coastal sea continuum: A case study of the Oujiang River

Author information +
文章历史 +

摘要

有机碳是河流-河口-近海连续体(以下简称连续体)碳循环的关键变量之一,厘清其时空分布特征及影响因素是开展碳循环研究的重要基础。本研究基于2023年2月(枯水季)和2023年7月(丰水季)的观测数据,分析了瓯江陆海连续体中颗粒有机碳(POC)和溶解有机碳(DOC)的含量、空间分布及季节变化特征。结果表明,无论是POC还是DOC,其在丰水季的质量浓度普遍高于枯水季。具体来看,枯水季POC质量浓度范围为0.43~20.56 mg/L,平均值为3.91 mg/L;丰水季POC质量浓度范围为0.15~32.78 mg/L,平均值为7.89 mg/L;枯水季DOC质量浓度范围为0.82~2.17 mg/L,平均值为1.37 mg/L;丰水季DOC质量浓度范围为1.35~3.80 mg/L,平均值为2.16 mg/L。从空间分布来看,POC质量浓度在河口段较高,在河流段和近海段较低;而DOC质量浓度则在河流段和河口段较高,在近海段相对较低。特别地,河口段的POC和DOC质量浓度均表现出对盐度的非保守性行为。综合分析盐度、总悬浮物质量浓度、最大浑浊带及其他环境因子,认为丰水季较高的降水量和径流量增强了流域的径流冲刷与侧向淋溶作用,是导致有机碳含量在丰水季高于枯水季的主要原因;而最大浑浊带的发育以及人类活动产生的有机质排放,则是有机碳在河口段富集的关键因素。

Abstract

Organic carbon is one of the key variables in the carbon cycle of the river-estuary-coastal continuum (hereinafter referred to as the “continuum”). Clarifying its spatiotemporal distribution characteristics and influencing factors is an important foundation for conducting carbon cycle research. Based on observational data in February 2023 (dry season) and July 2023 (wet season), this study analyzed the mass concentrations, spatial distribution, and seasonal variation characteristics of particulate organic carbon (POC) and dissolved organic carbon (DOC) in the continuum of the Oujiang River. The results showed that both POC and DOC generally exhibited higher mass concentrations in the wet season than those in the dry season. Specifically, the range of POC mass concentration in the dry season was 0.43-20.56 mg/L, with an average of 3.91 mg/L; in the wet season, the range was 0.15-32.78 mg/L, with an average of 7.89 mg/L. For DOC, the range in the dry season was 0.82-2.17 mg/L, averaging 1.37 mg/L, while in the wet season, it ranged from 1.35 to 3.80 mg/L, with an average of 2.16 mg/L. Spatially, POC mass concentration was higher in the estuarine section but lower in the riverine and coastal sections, whereas DOC mass concentration was relatively higher in the riverine and estuarine sections and lower in the coastal section. Notably, both POC and DOC mass concentrations in the estuarine section displayed non-conservative behavior with respect to salinity. Through comprehensive analysis of factors such as salinity, total suspended matter (TSM) mass concentration, the maximum turbidity zone, and other environmental variables, it is concluded that the increased precipitation and runoff during the wet season enhanced fluvial erosion and lateral leaching, which were the main reasons for the higher organic carbon content in the wet season compared to the dry season. Meanwhile, the development of the maximum turbidity zone and the input of organic matter from human activities were key factors contributing to the enrichment of organic carbon in the estuarine section.

关键词

河流-河口-近海连续体 / 溶解有机碳 / 颗粒有机碳 / 瓯江 / 空间分布 / 季节变化 / 丰水季 / 枯水季

Key words

river-estuary-coastal ocean continuum / dissolved organic carbon / particulate organic carbon / Oujiang River / spatial distribution / seasonal variation / wet season / dry season

引用本文

导出引用
申思远, 陆莎莎, 李中乔, . 河流-河口-近海连续体有机碳时空分布特征:以瓯江为例[J]. 海洋学研究. 2026, 44(2): 103-112 https://doi.org/10.3969/j.issn.1001-909X.2026.02.011
SHEN Siyuan, LU Shasha, LI Zhongqiao, et al. Spatial and temporal distribution characteristics of organic carbon in the river-estuary-coastal sea continuum: A case study of the Oujiang River[J]. Journal of Marine Sciences. 2026, 44(2): 103-112 https://doi.org/10.3969/j.issn.1001-909X.2026.02.011
中图分类号: P734   

参考文献

[1]
BATTIN T J, LAUERWALD R, BERNHARDT E S, et al. River ecosystem metabolism and carbon biogeochemistry in a changing world[J]. Nature, 2023, 613(7944): 449-459.
[2]
REGNIER P, RESPLANDY L, NAJJAR R G, et al. The land-to-ocean loops of the global carbon cycle[J]. Nature, 2022, 603(7901): 401-410.
[3]
刘志媛. 黄河河口过程中碳的行为变化[D]. 青岛: 中国海洋大学, 2011.
LIU Z Y. The changing behavior of carbon from estuarine dynamics in Yellow River estuary[D]. Qingdao: Ocean University of China, 2011.
[4]
刘志媛. 黄河口碳的输运特征及通量[D]. 青岛: 中国海洋大学, 2014.
LIU Z Y. Carbon transport and flux in the Yellow River estuary[D]. Qingdao: Ocean University of China, 2014.
[5]
张向上. 黄河口碳输运过程及其对莱州湾的影响[D]. 青岛: 中国海洋大学, 2007.
ZHANG X S. The transport of inorganic and organic carbon in the Yellow River estuary and its effect on Laizhou Bay[D]. Qingdao: Ocean University of China, 2007.
[6]
朱先进, 于贵瑞, 高艳妮, 等. 中国河流入海颗粒态碳通量及其变化特征[J]. 地理科学进展, 2012, 31(1):118-122.
摘要
河流是连接海洋和陆地两大碳库的纽带,其碳通量是全球碳循环的重要环节。本文以《中国河流泥沙公报》的数据为基础,就中国河流入海颗粒态碳通量及其变化特征进行分析。结果表明:1965-2005 年,中国河流入海颗粒态碳通量平均为29.57 TgC·yr<sup>-1</sup>,占河流入海碳通量的42%,其中有机碳占36.02%,无机碳占63.98%,长江、黄河和珠江的颗粒态碳通量占全国河流入海颗粒态碳通量的96.25%。从2003 年开始,河流入海颗粒态碳通量呈逐年递减的趋势,但颗粒态有机碳通量在河流入海颗粒态碳通量中所占的比重有所提高。2009 年,全国通过河流泥沙输送到海洋中的碳仅为6.59 TgC,为1965-2005 年平均输碳量的22.3%。由此可见,颗粒态碳通量在河流碳通量中占有不可忽视的地位,为了准确评估中国河流及陆地生态系统的碳收支,应对颗粒态碳通量进行细致研究。
ZHU X J, YU G R, GAO Y N, et al. Fluxes of particulate carbon from rivers to the ocean and their changing tendency in China[J]. Progress in Geography, 2012, 31(1): 118-122.
The river is the linkage of terrestrial and ocean carbon pools, the flux of which is a critical component of global carbon cycle. In this paper, The authors analyze the characteristics of the fluxes of particulate carbon from rivers to the ocean (FPC) in China and predicted their tendency based on the data obtained from <i>Bulletin of Chinese River Sediment</i>. The results indicate that, from 1965 to 2005, the annual mean FPC is 29.57TgC yr<sup>-1</sup>, 36.02% of which is organic carbon, and the rest is inorganic carbon. FPC accounts for 42% of the river carbon fluxes. The quantity of particulate carbon flux from the Yangtze River, the Yellow River and the Pearl River accounts for 96.25% of the total amount in China. There is a decreasing tendency of FPC since 2003, while the ratio of organic part to the total shows an increasing tendency. The FPC of 2009 is only 6.59TgC穣r<sup>-1</sup>, which is only 22.3% of the annual mean FPC from 1965 to 2005. Therefore, it is necessary to lay emphasis on the fluxes of particulate carbon in terms of its significant role in river carbon fluxes and terrestrial carbon budget.
[7]
陈鑫. 长江口及其邻近海域碳的迁移特征[D]. 青岛: 中国科学院研究生院(海洋研究所), 2014.
CHEN X. The carbon migration in the Changjiang estuary and adjacent sea[D]. Qingdao: Institute of Oceanology, Chinese Academy of Sciences, 2014.
[8]
陈建芳, 翟惟东, 王斌, 等. 河流-河口-近海连续体碳循环研究进展[J]. 海洋学研究, 2021, 39(4):11-21.
CHEN J F, ZHAI W D, WANG B, et al. A review of the carbon cycle in river-estuary-coastal ocean continuum[J]. Journal of Marine Sciences, 2021, 39(4): 11-21.
[9]
孙英, 蔡体录, 柴加龙, 等. 闽浙山溪性河口的径流特性及其对河口的冲淤影响[J]. 东海海洋, 1983, 1(2):29-35.
SUN Y, CAI T L, CHAI J L, et al. Runoff characteristics of mountain estuaries in Fujian and Zhejiang and its influence on erosion and deposition of estuaries[J]. Donghai Marine Science, 1983, 1(2): 29-35.
[10]
宋乐, 夏小明, 刘毅飞, 等. 瓯江河口入海水沙通量的变化规律[J]. 泥沙研究, 2012, 37(1):46-52.
SONG L, XIA X M, LIU Y F, et al. Variations in water and sediment fluxes from Oujiang River to estuary[J]. Journal of Sediment Research, 2012, 37(1): 46-52.
[11]
林伟波, 王义刚. 瓯江口海域悬浮泥沙输运特性研究[J]. 水力发电学报, 2013, 32(2):119-128.
LIN W B, WANG Y G. Study on characteristics of suspended sediment transport in Oujiang river estuary[J]. Journal of Hydroelectric Engineering, 2013, 32(2): 119-128.
[12]
张婉莹, 陆莎莎, 夏小明, 等. 瓯江汛期和非汛期水沙通量变化规律[J]. 海洋学研究, 2023, 41(2):61-70.
摘要
瓯江为典型的山溪性河流,其水沙通量具有洪枯季差异悬殊的特征。该文基于瓯江干流控制水文站71年(1950—2020年)月均径流量和43年(1956—1998年)月均输沙量观测资料,采用年内分配不均匀系数、Mann-Kendall非参数统计检验、双累积曲线等方法,分析了瓯江汛期(梅汛期4—6月和台汛期7—9月)和非汛期(10月—次年3月)水沙通量的变化规律及其原因。结果表明:1)径流量和输沙量的峰谷期一致,峰值出现在6月,谷值出现在12月,其中,梅汛期是瓯江的主汛期。2)1950—2020年瓯江径流量在梅汛期呈显著减少的趋势,在非汛期呈显著增加的趋势,在台汛期变化趋势不显著,径流量的年际变化主要受降水影响;径流量的年内分配趋于均匀化,受水库调蓄影响较大。3)1956—1998年瓯江输沙量在梅汛期呈显著减少的趋势,在台汛期和非汛期变化趋势不显著,其中梅汛期输沙量的减少与水库拦截有关;输沙量的年内分配不均匀性变化不大,可能与降水量的不均匀性变化有关。4)台汛期、非汛期的输沙量-径流量关系分别在1975年、1959年各发生了一次明显突变,均与流域内的强降水有关。
ZHANG W Y, LU S S, XIA X M, et al. Variations in water and sediment fluxes in Oujiang River during flooding and non-flooding seasons[J]. Journal of Marine Sciences, 2023, 41(2): 61-70.

Oujiang River is a typical mountain river whose water and sediment fluxes are characterized by a great disparity between flood and dry seasons. Based on the measured data of water discharge and sediment load at the mainstream control hydrological station of Oujiang River in the past 71 years (1950—2020) and 43 years (1956—1998), respectively, the coefficient of nonuniformity, Mann-Kendall non-parametric statistical test and double mass curve were used to analyze the variations of runoff and sediment load during the flood seasons (including plum rain season from April to June and typhoon season from July to September) and dry seasons (non-flooding season from October to March in next year) in the Oujiang River. The results showed that: (1) The peak and valley month of runoff were the same as sediment load. The peak month of both runoff and sediment load appeared in June, while their valley month appeared in December. The plum rain season was the most important period of water and sediment transporting to sea from Oujiang River. (2) The runoff showed significant decreasing trend in the plum rain season, significant increasing trend in non-flooding season, and non-significant trend in typhoon season during 1950—2020 in Oujiang River. The nonuniformity of intra-annual distribution for runoff had become more uniform obviously, resulting from the regulation of reservoirs. (3) The sediment load showed significant decreasing trend in the plum rain season due to the interception of reservoirs, and no significant trend in typhoon season and non-flooding season during 1956—1998 in Oujiang River. The nonuniformity of intra-annual distribution for sediment load showed little change, which might relate to the nonuniformity of intra-annual distribution for precipitation. (4) The relationship between sediment load and runoff during typhoon and non-flooding season changed in 1975 and 1959, respectively, both of which were related to the heavy rainfall within the river basins.

[13]
李玲, 薛峰, 张伯虎. 瓯江河口近期冲淤演变分析[J]. 浙江水利科技, 2020, 48(2):5-8.
LI L, XUE F, ZHANG B H. Analysis on recent erosion and deposition evolution of Oujiang River Estuary[J]. Zhejiang Hydrotechnics, 2020, 48(2): 5-8.
[14]
王雨航, 李尚清, 叶深, 等. 瓯江口海域浮游动物群落结构与环境因子的相关性分析[J]. 海洋学报, 2024, 46(3):98-110.
WANG Y H, LI S Q, YE S, et al. Correlation analysis of zooplankton community structure and environmental factors in the Oujiang River Estuary[J]. Haiyang Xuebao, 2024, 46(3): 98-110.
[15]
张能. 浙江省温州市瓯江及鳌江流域底栖动物群落结构与水生态质量评价[D]. 南京: 南京农业大学, 2022.
ZHANG N. Community structure of benthic macroinvertebrate and water ecological quality evaluation in Oujiang and Aojiang watershed of Wenzhou, Zhejiang Province[D]. Nanjing: Nanjing Agricultural University, 2022.
[16]
高少波, 池仕运, 李嗣新, 等. 楠溪江鱼类资源调查及物种多样性分析[J]. 水生态学杂志, 2017, 38(6):72-81.
GAO S B, CHI S Y, LI S X, et al. Fish resource investigation and species diversity analysis of Nanxi River in Zhejiang Province[J]. Journal of Hydroecology, 2017, 38(6): 72-81.
[17]
中华人民共和国生态环境部. 近岸海域环境监测技术规范第三部分近岸海域水质监测: HJ 442.3—2020[S]. 北京: 中国环境科学出版社, 2020.
The Ministry of Ecology and Environment of the People’s Republic of China. Technical specification for offshore environmental monitoring Part 3 offshore seawater quality monitoring: HJ 442.3—2020[S]. Beijing: China Environ-mental Science Press, 2020.
[18]
尚毅威. 南海北部海盆浮游植物和浮游动物的时空变化及其与颗粒有机碳输出的关系[D]. 厦门: 厦门大学, 2020.
SHANG Y W. Temporal-spatial variation of phytoplankton and zooplankton community and its relationship with the particulate organic carbon export in the northern South China Sea basin[D]. Xiamen: Xiamen University, 2020.
[19]
李宁, 李学刚, 宋金明. 海洋碳循环研究的关键生物地球化学过程[J]. 海洋环境科学, 2005, 24(2):75-80.
LI N, LI X G, SONG J M. Key biogeochemistry processes of marine carbon cycle[J]. Marine Environmental Science, 2005, 24(2): 75-80.
[20]
林晶. 长江口及其毗邻海区溶解有机碳和颗粒有机碳的分布[D]. 上海: 华东师范大学, 2007.
LIN J. Distributions of dissolved organic carbon and particulate organic carbon in the Changjiang estuary and its adjacent area[D]. Shanghai: East China Normal University, 2007.
[21]
张新周, 陈星, 窦希萍, 等. 山溪性强潮河口最大浑浊带形成机制及其模拟[J]. 水科学进展, 2019, 30(1):84-92.
ZHANG X Z, CHEN X, DOU X P, et al. Study on formation mechanism of turbidity maximum zone and numerical simulations in the macro tidal estuaries[J]. Advances in Water Science, 2019, 30(1): 84-92.
[22]
高成成. 山溪性河流河口有机碳来源、分布特征及其影响因素:以九龙江和漳江河口为例[D]. 厦门: 厦门大学, 2021.
GAO C C. Sources, distribution characteristics, and influencing factors of organic carbon in mountainous stream-type river estuaries: A case study of the Jiulong River and Zhangjiang River estuaries[D]. Xiamen: Xiamen University, 2021.
[23]
ZHANG S, GAN W B, ITTEKKOT V. Organic matter in large turbid rivers: The Huanghe and its estuary[J]. Marine Chemistry, 1992, 38(1/2): 53-68.
[24]
陶贞. 草原土壤有机碳动力学同位素示踪研究[D]. 广州: 中国科学院研究生院(广州地球化学研究所), 2005.
TAO Z. Isotope tracing of soil organic carbon dynamics in the grassland[D]. Guangzhou: Guangzhou Institute of Geochemistry, Chinese Academy of Sciences, 2005.
[25]
郭威, 叶丰, 连忠廉, 等. 珠江口水体有机碳的季节性变化[J]. 热带海洋学报, 2016, 35(4):40-50.
摘要
调查了珠江口不同季节颗粒有机碳(particulate organic carbon, POC)和溶解有机碳(dissolved organic carbon, DOC)含量的分布特征, 结合碳氮比值(C/N)、叶绿素a(Chl a)含量、溶解氧(dissolved oxygen, DO)含量等水化学参数, 探讨了珠江口POC、DOC来源、输送方式及混合行为的季节变化。结果表明, 珠江口水体POC可能主要受到水体自生浮游植物有机碳输入的影响, DOC可能主要来自于河流输送的陆源有机碳。在降雨量较大的5月份, POC来自自生浮游植物有机碳的贡献相对减小。降雨量同样较大的8月份DOC来自河流输送的陆源有机碳的贡献增加。不同季节珠江口水体总有机碳中的DOC一直高于POC。珠江口POC、DOC含量受到淡水与海水混合进程的影响, 淡水与海水的混合效应可能是从出虎门进入伶仃洋的低盐度区(盐度1&#x02030;~5&#x02030;的水体)开始延伸至外海。微生物的降解作用可能对POC和DOC在出虎门之前的下降趋势产生了重要影响, 而微生物对新鲜的浮游植物有机碳的利用、以及浮游植物生产量的降低和颗粒物絮凝沉降作用则可能是POC在出虎门后下降幅度大于DOC的重要原因。
GUO W, YE F, LIAN Z L, et al. Seasonal changes of organic carbon in the Pearl River estuary[J]. Journal of Tropical Oceanography, 2016, 35(4): 40-50.
Seasonal distributions of particulate organic carbon (POC) and dissolved organic carbon (DOC) concentrations, as well as their sources, transports and mixing behaviors, in the Pearl River estuary (PRE) are reported in this paper. Samples were collected in November 2013, and in February, May and August 2014. The results suggest that the sources of POC were mainly in situ aquatic phytoplankton, and the source of DOC was mainly input from terrigenous organic carbon. However, aquatic phytoplankton might have contributed less to POC in May than in other months due to intensified erosion by high rainfall during May, and terrigenous organic carbon contribution to DOC increased in August. DOC was always the main portion, i.e., higher than POC, in the total organic carbon. The conservative mixing process of riverine and marine organic carbon occurred from the low salinity zone (salinity of 1&#x02030;~5&#x02030;) near the Humen Outlet to the open sea area out of the PRE. Biological degradation may have played an important role in reducing POC and DOC concentrations in the upper reach of the Humen Outlet. Preferential consumption of fresh phytoplankton organic carbon, reduction of phytoplankton production, and flocculation and sinking of particulate matter might have collectively resulted in the much more reduction of POC than DOC in the upper reach.
[26]
包孝涵, 毕蓉, 朋鹏, 等. 2021年夏季珠江口颗粒有机碳空间分布特征及其影响因素[J]. 中国海洋大学学报:自然科学版, 2023, 53(12):71-84.
BAO X H, BI R, PENG P, et al. Spatial distributions and controlling factors of particulate organic carbon in the Pearl River Estuary in the summer of 2021[J]. Periodical of Ocean University of China, 2023, 53(12): 71-84.
[27]
LI Z, BAO X W, WANG Y Z, et al. Seasonal distribution and relationship of water mass and suspended load in North Yellow Sea[J]. Chinese Journal of Oceanology and Limnology, 2009, 27(4): 907-918.
[28]
张永领. 河流有机碳的输送特征对区域气候的响应[J]. 地球与环境, 2008, 36(4):348-355.
ZHANG Y L. The response of transport characteristics of riverine organic carbon to regional climate[J]. Earth and Environment, 2008, 36(4): 348-355.
[29]
刘诚刚, 宁修仁, 郝锵, 等. 海洋浮游植物溶解有机碳释放研究进展[J]. 地球科学进展, 2010, 25(2):123-132.
摘要
溶解有机碳(DOC)是海洋中最大的有机碳库,其中化学性质不稳定的成分大部分来自海洋浮游植物的释放。简要回顾了浮游植物溶解有机碳释放研究的发展历史,从光合作用合成的溶解有机碳(PDOC)释放占初级生产力的比重,PDOC的化学组成,浮游植物DOC释放的途径与机制,PDOC释放的环境调控,浮游植物群落组成对PDOC释放的影响,以及浮游植物释放DOC对异养细菌的生态意义等方面对相关研究进行了综述和分析。讨论了浮游植物溶解有机碳释放研究的现状和存在的问题,并对PDOC初级生产力测定的推广和相关研究的深化提出建议。
LIU C G, NING X R, HAO Q, et al. Advances in the study of photosynthetically produced dissolved organic carbon released of marine phytoplankton[J]. Advances in Earth Science, 2010, 25(2): 123-132.
[30]
刘金科, 韩贵琳, 阳昆桦, 等. 九龙江流域河水溶解态碳的时空变化[J]. 长江流域资源与环境, 2018, 27(11):2578-2587.
LIU J K, HAN G L, YANG K H, et al. Temporal and spatial variations of dissolved carbon in the Jiulongjiang River Basin[J]. Resources and Environment in the Yangtze Basin, 2018, 27(11): 2578-2587.
[31]
谭丽菊, 王江涛, 付强. 溶解有机碳在混合水中的行为研究[J]. 中国海洋大学学报:自然科学版, 2007, 37(5):811-814.
TAN L J, WANG J T, FU Q. The behavior of dissolved organic carbon(DOC) in mixtures of freshwater and seawater[J]. Periodical of Ocean University of China, 2007, 37(5): 811-814.

致谢

感谢自然资源部第二海洋研究所海洋生态系统动力学实验室为本次研究提供仪器支持,感谢浙江省温州市青田县水电有限公司提供径流量数据。

基金

国家自然科学基金联合基金(U23A2034)
国家自然科学基金(41576095)

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