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基于空间异质性分析的曹妃甸海草床密度量化分区及其形成机制

马旺 刘有才 张蒨 胡琦 陈衎 宋洪军

马旺,刘有才,张蒨,等. 基于空间异质性分析的曹妃甸海草床密度量化分区及其形成机制[J]. 海洋学报,2026,48(3):122–134 doi: 10.12284/hyxb2026024
引用本文: 马旺,刘有才,张蒨,等. 基于空间异质性分析的曹妃甸海草床密度量化分区及其形成机制[J]. 海洋学报,2026,48(3):122–134 doi: 10.12284/hyxb2026024
Ma Wang,Liu Youcai,Zhang Qian, et al. Density zoning and formation mechanism of seagrass beds in Caofeidian based on spatial heterogeneity analysis[J]. Haiyang Xuebao,2026, 48(3):122–134 doi: 10.12284/hyxb2026024
Citation: Ma Wang,Liu Youcai,Zhang Qian, et al. Density zoning and formation mechanism of seagrass beds in Caofeidian based on spatial heterogeneity analysis[J]. Haiyang Xuebao,2026, 48(3):122–134 doi: 10.12284/hyxb2026024

基于空间异质性分析的曹妃甸海草床密度量化分区及其形成机制

doi: 10.12284/hyxb2026024
基金项目: 中央引导地方科技发展资金项目“鳗草海草床空间展布机制及固碳增汇关键技术研究”(246Z3301G);中央引导地方科技发展资金项目“河北省海草床海洋碳汇能力核算方法研究”(226Z3301G);河北省地矿局科研项目“河北省蓝碳碳汇时空格局及演化集成研究”(13000025P003294103533)。
详细信息
    作者简介:

    马旺(1986—),男,河北省石家庄市人,高级工程师,主要研究方向为海洋环境。E-mail:skyhks@163.com

    通讯作者:

    宋洪军,副研究员,博士,主要从事海洋生态学领域研究。E-mail:songhongjun@fio.org.cn

  • 中图分类号: X22; X32

Density zoning and formation mechanism of seagrass beds in Caofeidian based on spatial heterogeneity analysis

  • 摘要: 以我国现存面积最大的曹妃甸海草床作为研究对象,采用遥感解译、现场调查和模型解析相结合的方法,开展了曹妃甸海草床密度量化分区及其空间异质性形成机制研究。通过高分辨率卫星遥感影像解译并结合现场实地验证,获得了曹妃甸海草床“北密南疏”分布格局下3类核心分区的量化数据(密集区:面积11.13 km2,占比26.03%;中等密集区:面积15.06 km2,占比35.23%;稀疏区:面积16.56 km2,占比38.74%),整体分布呈现出斑块化嵌合分布的特征。基于现场调查获取的光照、铵盐、底质密度等10项环境资料,运用多层感知器–人工神经网络(MLP-ANN)模型解析发现,底质内摩擦角(贡献率18%)、水体温度(贡献率15%)、底质磷酸盐(贡献率15%)是影响海草床密度分区的核心因子,且累计影响占比达48%。研究表明,曹妃甸海草床的密度分区是由自然动力因素与人为活动共同作用形成的:南部区域由于潮汐海流较强,导致底质遭受冲刷,同时叠加油田勘探、航道疏浚等工程活动以及陆源污染的影响,形成了“底质扰动–营养失衡”的退化链;北部区域远离这些扰动源,并且经过生态修复,底质条件得到优化,从而为中高密度海草床区域的形成提供了支撑。本研究填补了曹妃甸海草床密度分区量化研究及其机制研究方面的不足,为渤海湾海草床的科学评估及有效修复提供了科学依据和技术范式。
  • 图  1  曹妃甸海草床调查区域及站位

    Fig.  1  Investigation area and stations of seagrass beds in Caofeidian

    图  2  海草床分布区

    Fig.  2  Seagrass bed distribution area

    图  3  海草床不同密度区环境要素归一化后的变化范围

    归一化前原始指标单位:黏聚力(Pa)、内摩擦角(°)、深度(m)、温度(℃)、光照(μmol·m–2·s–1)、盐度、悬浮颗粒物(mg·L–1)、溶解氧(mg·L–1)、pH(无量纲)、NO2(μmol·L–1)、NO3(μmol·L–1)、PO4(μmol·L–1)、NH4(μmol·L–1)、粒度(μm)、密度(g·cm–3)、含水率(%)、容重(g·cm–3)、孔隙度(%)、有机质(%)、全氮(%)、硫化物(mg·kg–1

    Fig.  3  Environmental factors in different density zones of seagrass beds normalized variation range

    Original index units before normalization: Cohesion (Pa), Internal friction angle (°), Depth (m), Temperature (℃), Illumination (μmol·m–2·s–1), Salinity, Suspended particles (mg·L–1), Dissolved oxygen (mg·L–1), pH (Dimensionless), NO2 (μmol·L–1), NO3 (μmol·L–1), PO4 (μmol·L–1), NH4 (μmol·L–1), Grain size (μm), Density (g·cm–3), Moisture content (%), Bulk density (g·cm–3), Porosity (%), Organic matter (%), Total nitrogen (%), Sulfide (mg·kg–1)

    图  4  海草床密度的环境要素影响占比

    Fig.  4  The proportion of environmental factors influencing seagrass bed density

    图  5  曹妃甸海草床密度分区关键影响因子与保护修复策略概念图

    Fig.  5  Conceptual diagram of key influencing factors and protection-restoration strategies for density zoning of Caofeidian seagrass beds

    表  1  调查站位信息

    Tab.  1  Survey station information

    站位编号纬度/°N经度/°E所属区域类型
    B139.10212118.6554裸沙区
    B239.12145118.6846
    B339.12517118.7207
    B439.11416118.7636
    B539.07851118.6902
    B639.08105118.7428
    B739.04003118.6825
    B839.0638118.7153
    B939.02618118.7233
    S139.09862118.6828海草区
    S239.10263118.6687
    S339.09544118.6723
    S439.08691118.6758
    S539.04813118.7239
    S639.05451118.7092
    S739.04657118.7012
    S839.10457118.7158
    S939.08841118.7261
    S1039.1044118.7015
    S1139.11593118.7101
    S1239.10625118.7308
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  • 收稿日期:  2025-12-19
  • 修回日期:  2026-01-26
  • 网络出版日期:  2026-02-13
  • 刊出日期:  2026-03-25

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