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人类活动影响下亚热带岩溶河流水化学驱动机制与化学风化增强机制

王松 刘凡 侯涛 周振钊 李明 王子博 陈坚庆 郭芳

王 松,刘 凡,侯 涛,等. 人类活动影响下亚热带岩溶河流水化学驱动机制与化学风化增强机制−以滃江流域为例[J]. 中国岩溶,2026,45(3):1-15 doi: 10.11932/karst2025y031
引用本文: 王 松,刘 凡,侯 涛,等. 人类活动影响下亚热带岩溶河流水化学驱动机制与化学风化增强机制−以滃江流域为例[J]. 中国岩溶,2026,45(3):1-15 doi: 10.11932/karst2025y031
WANG Song, LIU Fan, HOU Tao, ZHOU Zhenzhao, LI Ming, WANG Zibo, CHEN Jianqing, GUO Fang. Hydrochemical Drivers and Enhanced Chemical Weathering Mechanisms of a Subtropical Karst River under Anthropogenic Influences: A Case Study of the Wengjiang River Basin[J]. CARSOLOGICA SINICA. doi: 10.11932/karst2025y031
Citation: WANG Song, LIU Fan, HOU Tao, ZHOU Zhenzhao, LI Ming, WANG Zibo, CHEN Jianqing, GUO Fang. Hydrochemical Drivers and Enhanced Chemical Weathering Mechanisms of a Subtropical Karst River under Anthropogenic Influences: A Case Study of the Wengjiang River Basin[J]. CARSOLOGICA SINICA. doi: 10.11932/karst2025y031

人类活动影响下亚热带岩溶河流水化学驱动机制与化学风化增强机制——以滃江流域为例

doi: 10.11932/karst2025y031
基金项目: 广东省水文环境地质调查中心科研项目(YRSF2024168);广西自然科学基金项目(2023GXNSFBA026254);国家自然科学基金项目(42302296));中国地质科学院基本科研业务费专项经费(JKYZD202414)
详细信息
    作者简介:

    王松,女,1983年,高级工程师,硕士研究生,研究方向为水文地质。E-mail:164290173@qq.com

    通讯作者:

    刘凡,男,1988年,副研究员,硕士研究生,研究方向为水文地质。E-mail:liufancags@126.com

  • 中图分类号: P641

Hydrochemical Drivers and Enhanced Chemical Weathering Mechanisms of a Subtropical Karst River under Anthropogenic Influences: A Case Study of the Wengjiang River Basin

  • 摘要: 为探讨高强度人类活动干扰下河流的水化学驱动机制及化学风化增强机制,以珠江水系北江一级支流滃江流域为研究对象,综合运用水化学和同位素图解,以及离子比值等方法,分析人类活动对亚热带季风气候区岩溶河流水化学的影响,使用外源阳离子干扰条件下的离子来源解析方法,剖析人类活动对水文地球化学的响应特征和风化过程的驱动作用,并揭示对化学风化的增强机制。结果表明,枯水期地下水对河流的补给比例增大,水化学呈现蒸发浓缩效应;碳酸盐岩风化主导水化学离子组成,人类活动的贡献在枯水期显著增加;计算得出流域化学风化速率为78.7 t·km−2·a−1,定量揭示硫酸的参与使风化速率提升了19.8%。本研究系统分析了高强度人类活动与地质背景、季节性水文变化之间的复杂协同作用,揭示了人类活动干扰下的流域水化学驱动机制和化学风化增强机制,为亚热带岩溶流域的地球化学循环提供科学参考。

     

  • 图  1  研究区地质地貌和采样点分布图

    Figure  1.  Geological and topographic map of the study area and location of sampling points

    图  2  水样中主要离子浓度分布和异常值图

    Figure  2.  Bar chart and outliers of main ion concentrations in water samples

    图  3  丰枯季δD和δ18O同位素箱线图

    Figure  3.  Box-plot of δ2H and δ18O in water samples for different seasons

    图  4  丰枯季δ2H和δ18O散点图和氘盈余箱线图

    Figure  4.  Scatter plot and box-plot of δ2H, δ18O and d-excess for different seasons

    图  5  丰枯季干流和主要支流的Piper三线图

    Figure  5.  Piper diagrams of the main stream and major tributaries during the wet and dry seasons

    图  6  丰枯季干流和主要支流的Gibbs图

    Figure  6.  Gibbs diagrams of the main stream and major tributaries during the wet and dry seasons

    图  7  离子摩尔浓度组合比值散点图

    Figure  7.  Scatter plot of molar concentration ratios

    图  8  丰枯季离子浓度相关性热图

    Figure  8.  Heatmap of ion concentration correlations during the wet and dry seasons

    图  9  岩石风化化学计量图

    Figure  9.  The chemometry diagram of rock weathering

    图  10  丰枯季阳离子的4种来源和贡献率

    Figure  10.  Contributions of 4 sources to the cation concentrations in water samples for different seasons

    表  1  研究区水样的主要理化参数表

    Table  1.   The physicochemical parameters of water samples in study area

    指标/单位 丰水期 枯水期
    最小值 最大值 均值 标准差 最小值 最大值 均值 标准差
    水温/℃ 22.90 31.20 28.04 2.09 14.82 19.40 17.22 1.30
    pH/无量纲 6.58 8.76 7.41 0.49 7.11 8.41 7.73 0.33
    EC/μS·cm−1 80.2 336.2 162.9 64.1 102.8 391.7 232.1 80.4
    K+/mmol·L−1 0.023 0.094 0.058 0.019 0.023 0.129 0.082 0.032
    Na+/mmol·L−1 0.042 0.420 0.147 0.088 0.040 1.164 0.286 0.310
    Ca2+/mmol·L−1 0.187 1.269 0.556 0.289 0.213 1.343 0.724 0.339
    Mg2+/mmol·L−1 0.044 0.285 0.103 0.054 0.058 0.318 0.144 0.067
    Cl/mmol·L−1 0.037 0.194 0.076 0.036 0.045 0.357 0.123 0.089
    ${\rm{SO}}_4^{2-}$/mmol·L−1 0.050 0.946 0.190 0.195 0.078 0.811 0.240 0.179
    ${\rm{HCO}}_3^{-}$/mmol·L−1 0.138 2.133 0.972 0.601 0.106 2.822 1.400 0.751
    ${\rm{NO}}_3^{-}$/mmol·L−1 0.004 0.396 0.123 0.144 未检出 0.642 0.116 0.168
    Si/mmol·L−1 0.084 0.374 0.232 0.094 0.123 0.371 0.239 0.086
    SIc (无量纲) −2.78 0.64 −1.01 0.96 −2.34 0.49 −0.54 0.75
    下载: 导出CSV
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  • 收稿日期:  2025-09-02
  • 录用日期:  2025-12-08
  • 修回日期:  2025-11-28
  • 网络出版日期:  2026-03-26

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