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基于OLCI数据的杭州湾悬浮物浓度估算及其产品适用性分析

李渊 郭宇龙 程春梅 张毅博 胡耀躲 夏忠 毕顺

李渊,郭宇龙,程春梅,等. 基于OLCI数据的杭州湾悬浮物浓度估算及其产品适用性分析[J]. 海洋学报,2019,41(9):156–169,doi:10.3969/j.issn.0253−4193.2019.09.015
引用本文: 李渊,郭宇龙,程春梅,等. 基于OLCI数据的杭州湾悬浮物浓度估算及其产品适用性分析[J]. 海洋学报,2019,41(9):156–169,doi:10.3969/j.issn. 0253−4193.2019.09.015
Li Yuan,Guo Yulong,Cheng Chunmei, et al. Remote estimation of total suspended matter concentration in the Hangzhou Bay based on OLCI and its water color product applicability analysis[J]. Haiyang Xuebao,2019, 41(9):156–169,doi:10.3969/j.issn.0253−4193.2019.09.015
Citation: Li Yuan,Guo Yulong,Cheng Chunmei, et al. Remote estimation of total suspended matter concentration in the Hangzhou Bay based on OLCI and its water color product applicability analysis[J]. Haiyang Xuebao,2019, 41(9):156–169,doi:10.3969/j.issn. 0253−4193.2019.09.015

基于OLCI数据的杭州湾悬浮物浓度估算及其产品适用性分析

doi: 10.3969/j.issn.0253-4193.2019.09.015
基金项目: 国家自然科学基金项目(41501374,41701422);浙江省自然科学基金项目(LQ16D010001)。
详细信息
    作者简介:

    李渊(1985—),男,山西省长治市人,副教授,主要从事水环境遥感研究。E-mail:liyuannjnu@163.com

    通讯作者:

    郭宇龙,讲师,主要从事水环境遥感研究。E-mail:gyl.18@163.com

  • 中图分类号: X87

Remote estimation of total suspended matter concentration in the Hangzhou Bay based on OLCI and its water color product applicability analysis

  • 摘要: 悬浮物含量及其时空分布是河口海岸环境中关心的热点问题。2016年2月16日,欧洲航天局发射了新一代海洋水色传感器(OLCI),该传感器具有良好的时空及光谱分辨率。本研究结合2017年7月杭州湾同步采样数据,对比了6种大气校正算法和8种悬浮物浓度(TSM)估算模型,遴选和分析了适宜于杭州湾和OLCI数据的大气校正方法和TSM估算模型,验证了OLCI数据二级产品精度和适用性。结果表明:(1)基于紫外光谱的大气校正算法(UVAC)精度最高,同步4个采样点的大气校正平均相对误差(MAPE)分别为34.21%、13.11%、5.92%和20.28%。在除Oa1以外的14个波段的MAPE均值为15.23%,Oa4至Oa10波段的MAPE低于8%;(2)基于Oa16/Oa5的波段比值模型,具有良好的建模(MAPE为16.49%,RMSE为50.92 mg/L)和验证(MAPE为19.08%,RMSE为19.29 mg/L)精度及模型稳健性;(3)基于C2RCC算法的固有光学量和TSM含量产品及OLCI二级TSM含量产品在杭州湾精度较差,不适用于杭州湾TSM和固有光学量遥感监测应用;(4)空间上,TSM在杭州湾中部区域含量较低,在杭州湾南岸和湾口区域含量较高。
  • 图  1  研究区及采样点分布示意

    Fig.  1  The location of study area and the spatial distribution of sampling stations

    图  2  杭州湾悬浮物浓度特征(a)及颗粒物吸收特性分析(b)

    Fig.  2  Characteristics of TSM (a) and absorption of suspended matter (b)

    图  3  遥感反射率与悬浮物浓度关系示意

    Fig.  3  The relationship between remote sensing reflectance and TSM

    图  4  不同方法大气校正精度评价

    Fig.  4  Evaluation of the accuracy of different atmospheric correction method

    图  5  基于C2RCC算法所得aph(443) (a)和ad(443) (b)的估算结果与实测值对比

    Fig.  5  The C2RCC-derived aph(443) (a) and ad(443) (b) are compared with in situ value, respectively

    图  6  基于C2RCC算法和OLCI Level 2产品的TSM估算结果与实测值对比

    Fig.  6  The C2RCC-derived TSM and OLCI Level 2 TSM are compared with measured TSM

    图  7  基于UVAC和C2RCC算法的TSM空间分布

    Fig.  7  Spatial distribution of TSM based on UVAC and C2RCC algorithm

    表  1  不同大气校正方法逐波段MAPE误差统计

    Tab.  1  Error statistics in each band of different atmospheric correction method

    波段(中心波长) 6S Flaash C2RCC MUMM BPAC UVAC
    Oa1(400 nm) 174.43% 118.94% 61.67% 70.46% 56.30% 62.39%
    Oa2(413 nm) 96.66% 53.00% 59.45% 72.68% 54.33% 32.88%
    Oa3(443 nm) 77.79% 64.59% 58.32% 55.37% 44.26% 20.95%
    Oa4(490 nm) 46.07% 31.41% 53.83% 43.93% 34.07% 7.67%
    Oa5(510 nm) 37.06% 23.53% 52.09% 41.24% 30.31% 4.81%
    Oa6(560 nm) 18.02% 10.56% 48.45% 28.25% 21.97% 4.93%
    Oa7(620 nm) 16.22% 13.77% 38.58% 21.45% 18.55% 6.09%
    Oa8(665 nm) 23.08% 18.11% 50.24% 18.45% 17.46% 6.85%
    Oa9(674 nm) 23.08% 18.53% 55.52% 17.47% 17.40% 6.69%
    Oa10(681 nm) 23.83% 19.14% 53.93% 28.23% 17.05% 7.06%
    Oa11(709 nm) 28.64% 26.72% 27.51% 29.95% 18.65% 16.89%
    Oa12(754 nm) 78.99% 70.45% 45.68% 30.47% 37.70% 14.66%
    Oa16(779 nm) 70.60% 62.73% 42.46% 29.17% 39.26% 16.24%
    Oa17(865 nm) 116.25% 114.58% 64.91% 39.70% 57.22% 31.13%
    Oa18(885 nm) 128.84% 137.43% 66.74% 47.37% 62.38% 36.43%
    下载: 导出CSV

    表  2  SERT模型中的参数αβ

    Tab.  2  The value of parameters α and β in SERT model

    波长/nm α β
    560 0.042 2 35.334 8
    620 0.064 3 0.147 6
    709 0.074 9 0.036 7
    779 0.086 7 0.007 6
    下载: 导出CSV

    表  3  基于实测数据构建的各类最优反演模型及精度评价

    Tab.  3  The various developed TSM retrieval algorithms and its accuracy assessment

    模型 公式 自变量 R2 MAPE/% RMSE/mg·L−1
    单波段 TSM = 10(27.761x + 1.421 2) Oa16 0.81 18.16 72.73
    波段比值 TSM = 10(1.057 5x + 1.327 5) Oa16/Oa5 0.90 16.49 50.92
    三波段 TSM = 10[2.049 2 + 9.686 4(x2 + x3)−0.149 8(x1/x2)] Oa1、Oa17、Oa18 0.87 18.87 65.88
    多元回归 TSM=10(1.860 1 − 36.829 3x1 + 17.577 2x2 + 27.753 4x3) Oa5、Oa7、Oa12 0.91 17.79 42.87
    SAI光谱指数 TSM = 10(1.827 7SAI + 1.007 2) Oa4、Oa6、Oa16 0.89 16.29 49.19
    SERT 24.56 62.07
    3S TSM = −1 911.7x + 26.924 [Oa11−1−Oa12−1]−1 0.92 18.68 52.17
    Nechad TSM = 910.02x − 7.624 7 Oa18/(0.093 − Oa18) 0.84 25.54 65.17
    下载: 导出CSV

    表  4  基于OLCI数据的模型精度评价

    Tab.  4  The accuracy assessment of various developed TSM retrieval algorithms based on OLCI data

    模型 斜率 截距 R2 MAPE/% RMSE/mg·L−1
    单波段 0.58 21.97 0.93 23.43 31.02
    波段比值 0.82 11.86 0.91 19.08 19.29
    三波段 0.66 −11.78 0.85 53.39 49.94
    多元回归 0.72 14.88 0.92 19.74 23.07
    SAI光谱指数 0.93 12.07 0.91 22.23 18.68
    SERT 0.78 −6.31 0.84 31.10 35.32
    3S 0.82 23.45 0.87 30.84 22.41
    Nechad 0.79 −3.53 0.83 33.73 33.83
    下载: 导出CSV

    表  5  模型在不同TSM浓度等级上的精度评价

    Tab.  5  The performance of various developed TSM retrieval algorithms on different TSM level

    模型 TSM<80 mg/L 80 mg/L≤TSM≤150 mg/L TSM>150 mg/L
    MAPE/% RMSE/mg·L−1 MAPE/% RMSE/mg·L−1 MAPE/% RMSE/mg·L−1
    单波段 16.25 12.38 22.54 45.70 34.29 107.20
    波段比值 14.71 10.97 14.60 22.94 21.35 68.46
    三波段 18.23 12.60 17.73 31.76 24.52 77.42
    多元回归 14.99 10.75 15.72 23.57 19.63 45.76
    SAI光谱指数 17.26 13.19 14.49 23.24 20.94 51.45
    SERT 25.53 17.22 26.07 59.43 34.67 81.86
    3S 26.83 16.47 16.73 31.61 22.61 58.70
    Nechad 26.74 16.71 26.79 51.70 31.58 78.43
    下载: 导出CSV

    表  6  模型敏感性分析

    Tab.  6  The sensitivity analysis of three developed TSM retrieval algorithms

    模型 MAPE/% RMSE/mg·L−1
    范围 均值 范围 均值
    波段比值 16.34~16.62 16.50 50.14~51.83 51.02
    多元回归 50.99~62.23 55.88 108.66~182.18 141.75
    SAI光谱指数 16.20~16.66 16.43 48.74~50.22 49.42
    下载: 导出CSV
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  • 收稿日期:  2018-08-15
  • 修回日期:  2018-11-01
  • 网络出版日期:  2021-04-21
  • 刊出日期:  2019-09-25

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