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贵州省湿地碳储量与碳中和潜力分析

张美琪 陈波 赵敏

张美琪, 陈波, 赵敏. 贵州省湿地碳储量与碳中和潜力分析[J]. 地质科技通报, 2023, 42(2): 315-326. doi: 10.19509/j.cnki.dzkq.tb20220358
引用本文: 张美琪, 陈波, 赵敏. 贵州省湿地碳储量与碳中和潜力分析[J]. 地质科技通报, 2023, 42(2): 315-326. doi: 10.19509/j.cnki.dzkq.tb20220358
Zhang Meiqi, Chen Bo, Zhao Min. Analysis of the carbon stock and carbon neutral potential of wetlands in Guizhou Province[J]. Bulletin of Geological Science and Technology, 2023, 42(2): 315-326. doi: 10.19509/j.cnki.dzkq.tb20220358
Citation: Zhang Meiqi, Chen Bo, Zhao Min. Analysis of the carbon stock and carbon neutral potential of wetlands in Guizhou Province[J]. Bulletin of Geological Science and Technology, 2023, 42(2): 315-326. doi: 10.19509/j.cnki.dzkq.tb20220358

贵州省湿地碳储量与碳中和潜力分析

doi: 10.19509/j.cnki.dzkq.tb20220358
基金项目: 

贵州省科技计划项目 黔科合支撑[2021]一般456

贵州财经大学校级科研基金项目 2022KYQN05

详细信息
    作者简介:

    张美琪(1998—), 女, 现正攻读土地资源管理专业硕士学位, 主要从事土地生态治理与碳中和研究工作。E-mail: 1489777839@qq.com

    通讯作者:

    陈波(1990—), 男, 副教授, 主要从事气候变化与岩溶作用碳循环、土地生态治理与碳中和研究工作。E-mail: bobchen@mail.gufe.edu.cn

  • 中图分类号: X141

Analysis of the carbon stock and carbon neutral potential of wetlands in Guizhou Province

  • 摘要:

    湿地作为缓解气候变化的关键生态系统, 在碳捕获与碳封存方面发挥着不可替代的作用。湿地碳储量和影响因素的分析以及固碳潜力的预测, 对湿地生态保护与管理、国家"双碳"目标实现具有重要意义。应用ArcGIS10.8对《贵州省湿地保护发展规划》(以下简称规划)的3个时期(分别是: 1999-2009年; 2010-2018年; 2018年至今)湿地分布图采用遥感目视解译的方式进行矢量化并根据贵州省岩溶发育强度进行分区。采用生命带研究法与生物量估算法等对贵州省湿地面积和碳储量变化进行估算分析, 对重要湿地碳储量与单位面积碳储量进行估算并与全省湿地进行对比, 采用固碳潜力计算模型对贵州省重要湿地固碳潜力进行估算, 应用Origin软件对各相关影响因子进行数据分析。结果表明: ①贵州省湿地规划前期的面积为216 526.95 hm2, 规划中期面积为209 726.85 hm2、规划后期面积为255 440.53 hm2, 总体表现为先下降再升高, 总体面积增加38 913.58 hm2; ②贵州省湿地碳储量变化为: 规划前期为5.97×105 t, 规划后期为3.78×106 t, 是规划前期的6倍以上, 碳储量增加明显。其中, 贵州省重要湿地碳储量为3.24×106 t, 占全省湿地碳储量85.71%, 固碳潜力十分显著; ③贵州省重要湿地的固碳潜力为1.14×104 t C/a, 预计到2030和2060年, 湿地总固碳量分别达到7.99×106 t C和8.34×106 t C; ④温度、DIC浓度、有机碳含量与面积对贵州省重要湿地的碳储量影响较大, 重要湿地碳储量与DIC浓度、有机碳含量以及面积呈正相关, 而与温度呈负相关关系。对贵州省的湿地碳储量估算与碳中和潜力分析不仅可以了解贵州省湿地碳封存现状, 还可为区域湿地生态系统在"3060"双碳目标的贡献上提供理论参考。

     

  • 图 1  规划后湿地(a)与重要湿地(b)

    Figure 1.  Post-planning wetlands (a) and the key wetlands (b)

    图 2  贵州省不同类型湿地碳储量变化图

    Figure 2.  Changes in carbon stocks in different types of wetlands in Guizhou Province

    图 3  贵州省重要湿地碳储量位点图

    Figure 3.  Site map showing carbon stock in the key wetlands in Guizhou Province

    图 4  贵州省重要湿地固碳潜力位点图

    Figure 4.  Carbon sequestration potential site map of key wetlands in Guizhou Province

    图 5  贵州省岩溶地貌发育等级

    Figure 5.  Grade of karst landform development in Guizhou Province

    图 6  贵州省重要湿地碳密度和碳储量影响因子相关性分析

    Figure 6.  Correlation analysis of carbon density and carbon stock influence factors in the key wetlands in Guizhou Province

    表  1  贵州省不同类型湿地面积变化

    Table  1.   Changes in the area of different types of wetlands in Guizhou Province

    湿地类型 时期 面积/hm2 占比/%
    河流湿地 规划前期 166 351.16 76.83
    规划中期 138 154.76 65.87
    规划后期 147 089.20 57.58
    湖泊湿地 规划前期 - -
    规划中期 2 517.70 1.21
    规划后期 3 637.40 1.42
    沼泽湿地 规划前期 - -
    规划中期 10 978.70 5.23
    规划后期 5 213.93 2.04
    人工湿地 规划前期 50 175.79 23.17
    规划中期 58 075.69 27.69
    规划后期 99 500.00 38.95
    下载: 导出CSV

    表  2  贵州省重要湿地面积

    Table  2.   Area of key wetlands in Guizhou Province

    湿地 湿地类型 湿地面积/hm2 占比/%
    自然 河流湿地 37 710.21 73.69
    湖泊湿地 3 637.40 7.11
    沼泽湿地 5 213.93 10.19
    人工 人工湿地 4 615.40 9.02
    总和 51 176.85 100.00
    下载: 导出CSV

    表  3  计算数据及来源

    Table  3.   Data used for calculation and their sources

    时期 数据名称 数值 数据来源
    规划前 湿地面积/hm2 216 526.95 文献[14]
    HCO3-质量浓度/(mg·L-1) 177.52 文献[17]
    湖泊植被碳储量/t C 818.40 文献[18]
    土壤碳密度(0~100 cm)/(kg C·m-2) 11.44 文献[16]
    河流径流量/亿m3 993.35 文献[37]
    规划中 湿地面积/hm2 209 726.85 文献[14]
    HCO3-质量浓度/(mg·L-1) 168.89 文献[25-29]
    DOC质量浓度/(mg·L-1) 6.62 文献[19]
    湖泊植被生物量/(g·L-1) 107.00 试验数据
    沼泽植被碳密度/(kg C·m-3) 3.71 文献[16]
    河流径流量/亿m3 977.75 文献[37]
    土壤碳密度(0~100 cm)/(kg C·m-2) 5.57 文献[16]
    土壤容重/(g·cm-3) 1.42 文献[15]
    土壤CO2质量分数/(g·kg-1) 3.08 文献[15]
    土壤厚度/cm 94.49 文献[15]
    石砾体积分数/% 6.79 文献[15]
    规划后 湿地面积/hm2 255 440.53 文献[38-39]
    HCO3-质量浓度/(mg·L-1) 228.49 文献[22-24]
    DOC质量浓度/(mg·L-1) 6.62 文献[19]
    植被碳密度/(kg C·m-2) 37.33 文献[31]
    河流径流量/亿m3 1 141.44 文献[37]
    土壤容重/(g·cm-3) 1.19 文献[30]
    土壤CO2质量分数/(g·kg-1) 19.42 文献[30]
    土壤厚度/cm 37.23 文献[30]
    石砾体积分数/% 37.79 文献[30]
    植被碳密度/(kg C·m-2) 39.31 文献[31]
    下载: 导出CSV

    表  4  贵州省湿地碳储量变化

    Table  4.   Changes in wetland carbon stock in Guizhou Province

    湿地类型 时期 单位面积碳储量/(g C·m-1) 总碳储量/t
    河流湿地 规划前期 10.58 1.76×104
    规划中期 11.95 1.65×104
    规划后期 17.74 2.61×104
    湖泊湿地 规划前期 - -
    规划中期 29 530 7.44×105
    规划后期 24 080 8.76×105
    沼泽湿地 规划前期 - -
    规划中期 7 420.00 8.15×105
    规划后期 44 640.00 2.33×106
    人工湿地 规划前期 1 150.00 5.79×105
    规划中期 569.85 3.31×105
    规划后期 550.75 5.48×105
    下载: 导出CSV

    表  5  贵州省湿地总碳储量变化

    Table  5.   Changes in total carbon stock of wetlands in Guizhou Province

    时期 单位面积碳储量/(g C·m-2) 总碳储量/t
    规划前期 275.72 5.97×105
    规划中期 910.71 1.91×106
    规划后期 1 480.00 3.78×106
    下载: 导出CSV

    表  6  贵州省重要湿地固碳潜力

    Table  6.   Carbon sequestration potential of the key wetlands in Guizhou Province

    湿地类型 面积/hm2 固碳速率/(g C·m-2a-1) 固碳潜力/(t C·a-1)
    河流湿地 37 710.12 22.49 8 480
    湖泊湿地 3 637.40 20.08 730
    沼泽湿地 5 213.93 24.80 1 293
    人工湿地 4 615.40 22.49 1 038
    总和 51 176.85 11 541
    下载: 导出CSV

    表  7  贵州省湿地退耕还湖还泽固碳潜力

    Table  7.   Carbon sequestration potential of wetlands in Guizhou Province after returning farmland to lake and swamp

    恢复措施 面积潜力/(hm2·a-1) 固碳潜力/(t C·a-1)
    退耕还湖 33.64 6.82
    退耕还泽 47.12 11.69
    下载: 导出CSV

    表  8  贵州省湿地保护工程固碳潜力

    Table  8.   Carbon sequestration potential of wetland protection projects in Guizhou Province

    湿地类型 面积潜力/(hm2·a-1) 固碳潜力/(t C·a-1)
    河流湿地 626.330 1 140.86
    湖泊湿地 60.413 8 12.13
    沼泽湿地 86.598 5 21.48
    人工湿地 76.657 5 15.58
    总和 850.000 0 190.05
    下载: 导出CSV
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