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    中国湿地甲烷排放对二氧化碳吸收的抵消效应及机制

    Study on the offset effect and mechanism of methane emissions to carbon dioxide uptake in China's wetlands

    • 摘要:
      目的 准确量化并提升湿地对大气二氧化碳(CO2)的吸收能力是应对全球气候变暖的重要举措之一。然而,湿地吸收CO2的同时也会排放另外一种全球增温潜势更大的温室气体甲烷(CH4)。系统厘清不同时间尺度、不同湿地类型CH4年排放量对CO2年吸收量的抵消效应,有助于避免对湿地碳汇功能的“单一碳汇”误判,从而科学认知其综合气候效应。
      方法 本研究利用整合分析方法,系统收集并整理了我国内陆湿地和滨海湿地共计141个站点全年监测的生态系统净CO2交换量(NEE)数据,以及41个站点全年CH4排放量数据。
      结果 研究结果表明:(1)湿地类型上,所有湿地均表现为大气CO2的汇(负通量代表汇,负值越小表示汇越强),年NEE值排序为滨海红树林湿地(–29 672(–32 228 ~ –27 391)kg/hm2) < 滨海草本湿地(–12 029(–15 078 ~ –9 173)kg/hm2) < 内陆草本湿地(–8 819(–10 786 ~ –6 941)kg/hm2) < 富营养泥炭地(–5 006(–6 520 ~ –3 480)kg/hm2) < 贫营养泥炭地(–4 745(–7 136 ~ –2 452)kg/hm2);所有湿地均表现为大气CH4的源,年CH4排放量则表现为富营养泥炭地(437(385 ~ 483)kg/hm2)、内陆草本湿地(319(228 ~ 404)kg/hm2)显著高于滨海草本湿地(120(75 ~ 165)kg/hm2)、贫营养泥炭地(91(74 ~ 113)kg/hm2)及滨海红树林湿地(87(53 ~ 126)kg/hm2)(数值表示为平均值及其95%置信区间,下同)。(2)地理位置上,滨海湿地的年NEE(–19 719(–22 420 ~ –16 940)kg/hm2)显著低于内陆湿地(–6 215(–7 384 ~ –5 052)kg/hm2);而滨海湿地的年CH4排放量(96(63 ~ 130)kg/hm2)约为内陆湿地(282(222 ~ 345)kg/hm2)的三分之一。(3)气候带上,亚热带湿地的年NEE(–24 992(–27 590 ~ –22 428)kg/hm2)显著低于温带湿地(–6 237(–7 372 ~ –5 147)kg/hm2),而温带湿地的年CH4排放量(390(323 ~ 449)kg/hm2)显著高于亚热带湿地(109(86 ~ 133)kg/hm2)。(4)植被功能群上,以森林植物(–29 672(–32 198 ~ –27 434)kg/hm2)或禾本科植物(–11 646(–14 052 ~ –9 396)kg/hm2)为主的湿地,其年NEE显著低于以藓类(–7 036(–10 564 ~ –3 350)kg/hm2)或莎草科植物(–4 954(–6103 ~ –3 800)kg/hm2)为主的湿地,但年CH4排放量则是莎草科植物(410(337 ~ 471)kg/hm2)为主的湿地最高,其次是以禾本科植物(259(175 ~ 347)kg/hm2)为主的湿地,而以藓类(90(72 ~ 115)kg/hm2)和森林植物(87(53 ~ 127)kg/hm2)为主的湿地最低。此外,本研究也表明中国自然湿地中年CO2吸收量和CH4排放量随纬度递增、经度呈抛物线变化趋势。环境因子对年CO2吸收量和CH4排放量影响存在差异,年CO2吸收量随年平均气温(MAT)、降水量(MAP)等7项指标增加均线性增加,而年CH4排放量随MAT、MAP、盐度线性降低,随地下水位深度呈抛物线变化且水位在地表以下20 cm至接近地表的0 cm范围内达排放峰值,随土壤有机碳含量(SOC)的增加而呈对数递增趋势。在20 ~ 500年不同时间尺度上,年CO2吸收量和CH4排放量的净辐射平衡均随经度先降后升高且均随MAT、MAP、土壤温度、地下水位深度增加而线性降低,增温效应随之减弱。
      结论 就净辐射平衡时间动态变化而言,在20 ~ 100年尺度上,CH4排放可完全抵消内陆湿地、部分抵消滨海湿地的CO2吸收;而在500年尺度上,CH4排放仅能部分抵消内陆湿地的CO2吸收,对滨海湿地CO2吸收的抵消作用则微乎其微。因此,从长期视角来看,我国内陆湿地和滨海湿地均是持续性的含碳温室气体的净汇,且单位面积尺度上滨海湿地在应对气候变化方面的效果优于内陆湿地。

       

      Abstract:
      Objective Maximizing carbon dioxide (CO2) uptake in wetlands is part of the global effort to combat climate warming. Yet, the simultaneously emitted potent greenhouse gas methane (CH4) from wetlands may counterbalance their CO2 uptake potentially. Studying the offset effect of annual CH4 emissions to annual CO2 uptake across different time scales and across different types of wetlands can avoid the misjudgment of “single carbon sink”, is conducive to fully understanding the carbon sink function of wetlands.
      Method In this study, using the meta-analysis method, 141 years of data on net ecosystem CO2 exchange (NEE) and 41 years of data on CH4 fluxes were collated from different types of natural wetlands in China, including inland peatlands, marshes, coastal marshes, and mangroves.
      Result We find that, in terms of wetland types, all wetlands function as net sinks for atmospheric CO2 (negative flux represents sink and a smaller negative value indicates a stronger sink), and annual NEE increased following the order of coastal mangroves (–29 672 (–32 228 ~ –27 391) kg/ha), coastal marshes (–12 029 (–15 078 ~ –9 173) kg/ha), inland marshes (–8 819 (–10 786 ~ –6941) kg/ha), fens (–5 006 (–6 520 ~ –3 480) kg/ha), and peatland bogs (–4 745 (–7 136 ~ –2 452) kg/ha), while all wetlands function as net sources for atmospheric CH4, and annual CH4 emission rates were significant greater from peatland fens (437 (385 ~ 483) kg/ha) and inland marshes (319 (228 ~ 404) kg/ha) than those from coastal marshes (120 (75 ~ 165) kg/ha), peatland bogs (91 (74 ~ 113) kg/ha) and coastal mangroves (87 (53 ~ 126) kg/ha) (data is indicated as mean with 95% confidence interval, the same below). For the wetland location, annual NEE of coastal wetlands (–19 719 (–22 420 ~ –16 940) kg/ha) is significantly lower about two times than inland wetlands (–6 215 (–7 384 ~ –5 052) kg/ha) while annual CH4 emission rate from coastal wetlands (96 (63 ~ 130) kg/ha) is approximately one-third of inland wetlands (282 (222 ~ 345) kg/ha). With regard to the climate zone, subtropical wetlands (–24 992 (–27 590 ~ –22 428) kg/ha) showed significant lower annual NEE than temperate wetlands (–6 237 (–7 372 ~ –5 147) kg/ha), while annual CH4 emissions are significant greater for temperate wetlands (390 (323 ~ 449) kg/ha) than subtropical wetlands (109 (86 ~ 133) kg/ha). Considering the plant functional group, wetlands dominated by the forest (–29 672 (–32 198 ~ –27 434) kg/ha) or graminoid species (–11 646 (–14 052 ~ –9 396) kg/ha) showed significant lower annual NEE than wetlands dominated by moss (–7 036 (–10 564 ~ –3 350) kg/ha) or sedge species (–4 954 (–6 103 ~ –3 800) kg/ha), while annual CH4 emissions is greatest in wetlands dominated by sedge species (410 (337 ~ 471) kg/ha), followed by graminoid species (259 (175 ~ 347) kg/ha) and lowest in wetlands dominated by moss (90 (72 ~ 115) kg/ha) and forest species (87 (53 ~ 127) kg/ha). Moreover, annual CO2 uptake rates were significantly decreased and CH4 emission rates were significantly increased with the increasing latitudes from 20°N to 55°N while exhibited parabolic trend with longitudes across natural wetlands in China. There exist distinct differences in the impacts of environmental factors on annual CO2 uptake rates and CH4 emission rates. Annual CO2 uptake rates exhibits a linear increase with the increase of seven indicators, including mean annual temperature (MAT) and mean annual precipitation (MAP). In contrast, annual CH4 emissions decrease linearly with MAT, MAP, and salinity; display a parabolic variation with water table depth (WTD), peaking within the range of 20 cm below the soil surface to 0 cm of soil surface; and show a logarithmic increasing trend with the increase of soil organic carbon (SOC) content. Across time scales spanning from 20 to 500 years, the net radiation balance of CO2 uptake rates and CH4 emission rates first decreases and then increases with longitude, while both linearly decline with the increase of MAT, MAP, soil temperature (Ts), and WTD, accompanied by a corresponding weakening of the warming effect.
      Conclusion In conclusion, from the perspective of temporal variations of net radiative forcing, the positive radiative forcing of annual CH4 emissions can completely and partially offset the negative radiative forcing of annual CO2 uptake from inland and coastal wetlands, respectively, over 20- to 100-yr timeframes, while partially and marginally offset CO2 uptake from inland and coastal wetlands, respectively, over 500-yr timeframe. Therefore, inland and coastal wetlands function as persistently C-based net greenhouse gas sinks from the long-term perspective and the latter is more effective natural climate solutions than the former on a per-unit-area basis.

       

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