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基于GAM的西北太平洋日本鲭资源丰度预测模型建立

武胜男 陈新军 刘祝楠

武胜男,陈新军,刘祝楠. 基于GAM的西北太平洋日本鲭资源丰度预测模型建立[J]. 海洋学报,2019,41(8):36–42,doi:10.3969/j.issn.0253−4193.2019.08.004
引用本文: 武胜男,陈新军,刘祝楠. 基于GAM的西北太平洋日本鲭资源丰度预测模型建立[J]. 海洋学报,2019,41(8):36–42,doi:10.3969/j.issn.0253− 4193.2019.08.004
Wu Shengnan,Chen Xinjun,Liu Zhu'nan. Establishment of forecasting model of the abundance index for chub mackerel ( Scomber japonicus) in the northwest Pacific Ocean based on GAM[J]. Haiyang Xuebao,2019, 41(8):36–42,doi:10.3969/j.issn.0253−4193.2019.08.004
Citation: Wu Shengnan,Chen Xinjun,Liu Zhu'nan. Establishment of forecasting model of the abundance index for chub mackerel ( Scomber japonicus ) in the northwest Pacific Ocean based on GAM[J]. Haiyang Xuebao,2019, 41(8):36–42,doi:10.3969/j.issn.0253− 4193.2019.08.004

基于GAM的西北太平洋日本鲭资源丰度预测模型建立

doi: 10.3969/j.issn.0253-4193.2019.08.004
基金项目: 海洋局公益性行业专项(20155014);上海市科技创新计划(15DZ1202200)。
详细信息
    作者简介:

    武胜男(1994—),女,山东省青岛市人,主要从事渔业资源研究。E-mail:374723906@qq.com

    通讯作者:

    陈新军(1967—),教授,研究方向为渔业资源。E-mail:xjchen@shou.edu.cn

  • 中图分类号: S931.4

Establishment of forecasting model of the abundance index for chub mackerel (Scomber japonicus) in the northwest Pacific Ocean based on GAM

  • 摘要: 日本鲭(Scomber japonicus)是西北太平洋重要的鱼类资源之一,科学预测日本鲭的资源丰度有利于其资源的合理开发和利用。本研究依据日本渔业机构提供的1987–2012年日本鲭太平洋群体的资源量数据,结合产卵场和渔场的海洋环境数据以及气候因子,使用广义加性模型对影响日本鲭太平洋群体的海洋环境和气候因子进行分析,筛选出有显著影响的因子并建立该群体的资源量预测模型。结果表明,与该群体资源量有显著关系的影响因子有:北极涛动指数、太平洋年代际振荡指数、渔场海表面高度、渔场海表面盐度和渔场海表面温度。基于赤池信息准则筛选出的4个资源量预测模型分析表明,包含北极涛动指数、渔场海表面高度和渔场海表面温度的模型有较好的预测效果,该模型的验证结果也通过了t检验(P<0.05),可用于日本鲭太平洋群体资源量的预测。
  • 图  1  日本鲭太平洋群体分布区域图

    Fig.  1  Distribution of the Pacific-cohort of chub mackerel (Scomber japonicus)

    图  2  2000–2012年日本鲭太平洋群体资源量以及4种预测模型结果

    Fig.  2  The actual ln(Biomass) and the results of biomass forecasting models for the Pacific-cohort of chub mackerel (Scomber japonicus) during 2000–2012

    表  1  1987-1999年各环境因子和气候因子与日本鲭资源量的GAM检验

    Tab.  1  Test of GAM between the environmental or climatic factors and the biomass during 1987–1999

    影响因子PR2
    AOI0.05*0.24
    NI0.180.24
    PDOI2.64×10–5*0.76
    SOI0.150.27
    产卵场SSH(SSH1)/cm0.300.17
    渔场SSH(SSH2)/cm0.03*0.68
    产卵场SSS(SSS1)0.090.16
    渔场SSS(SSS2)3.00×10–3*0.96
    产卵场SST(SST1)/℃0.100.16
    渔场SST (SST2)/℃1.00×10–3*0.86
    黑潮潮差/m0.600.06
    亲潮春季平均面积/m20.280.20
      注:*表示在显著性水平α=0.05(双侧)上显著相关。
    下载: 导出CSV

    表  2  1987-1999年各关键影响因子之间的回归分析

    Tab.  2  Regression analysis of significant factors during 1987-1999

    影响因子PR2
    AOI,PDOI0.070.28
    AOI,SSH20.490.04
    AOI,SST20.140.19
    AOI,SSS20.420.06
    PDOI,SSH24.37×10–3*0.54
    PDOI,SST27.37×10–4*0.66
    PSO,SSS20.730.01
    SSH2,SST20.060.28
    SSH2,SSS20.490.04
    SST2,SSS20.937.08×10–4
      注:*表示在显著性水平α=0.05(双侧)上显著相关。
    下载: 导出CSV

    表  3  1987-1999年基于环境因子和气候因子的资源量预测模型

    Tab.  3  Forecasting models of biomass based on environmental and climatic factors during 1987–1999

    模型AICP值 (P<0.05)调整后的R2
    模型1–90.892 552.80×10–5*1.000
    模型2–79.380 894.41×10–3*0.999
    模型3–47.796 146.22×10–9*0.995
    模型4–24.670 129.97×10–8*0.970
      注:*表示在显著性水平α=0.05(双侧)上显著相关。
    下载: 导出CSV

    表  4  2000-2012年资源量的预测值和真实值之间的t检验

    Tab.  4  t test between the predicted ln(Biomass) and the actual ln(Biomass) during 2000–2012

    模型t自由度P值 (P<0.05)
    模型12.9718.338.08×10–3*
    模型24.2723.882.66×10–4*
    模型31.6320.900.12
    模型41.0120.730.33
      注:*表示在显著性水平α=0.05(双侧)上显著相关。
    下载: 导出CSV
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  • 收稿日期:  2018-06-04
  • 修回日期:  2018-07-17
  • 网络出版日期:  2021-04-21
  • 刊出日期:  2019-08-25

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