Kasak Kuno, Ahmadi Arman, Dronova Iryna, Arias-Ortiz Ariane, Wang Tianxin, Valach Alex C, Szutu Daphne, Verfaillie Joseph, Baldocchi Dennis D
Department of Environmental Science Policy and Management, University of California Berkeley, Berkeley, California, USA.
Department of Geography, University of Tartu, Tartu, Estonia.
Glob Chang Biol. 2026 Jan;32(1):e70700. doi: 10.1111/gcb.70700.
Globally, wetlands can sequester and store large amounts of soil carbon over the long term due to high primary productivity and slow decomposition. Yet centuries of drainage for agriculture and development have turned many of these carbon sinks into greenhouse gas (GHG) sources. Restoring degraded wetlands, particularly in peat-rich landscapes, is increasingly promoted as a nature-based solution for climate change mitigation. However, the trajectory and timing of recovery remain uncertain, especially given the complex interplay among vegetation dynamics, hydrology, and GHG fluxes. In this study, we analyzed 44 site-years of continuous eddy covariance measurements of carbon dioxide (CO) and methane (CH) fluxes from restored wetlands in California's Sacramento-San Joaquin Delta. Our findings reveal substantial interannual variability in GHG exchange across sites, driven by differences in restoration design, water management, and vegetation establishment. While rapid vegetation growth, especially dense stands of macrophytes, can enhance CO uptake, it often elevates CH emissions and complicates predictions of when wetlands become net GHG sinks. Crucially, wetlands with delayed vegetation establishment due to high or inconsistent water levels (e.g., significant drawdown) remained persistent GHG sources, even years after restoration. Conversely, sites with tailored planting or natural and rapid recolonization exhibited earlier transitions to net sink status, including earlier shifts towards net negative radiative forcing since the restoration. The study highlights the importance of adaptive, site-specific restoration strategies and long-term monitoring to capture switchover dynamics from sources to sinks. As global investment in wetland restoration grows, our findings underscore the need to balance climate mitigation goals with ecological realities and the self-designing processes of vegetation succession.
在全球范围内,由于初级生产力高且分解缓慢,湿地能够长期固存和储存大量土壤碳。然而,数百年来为了农业和发展而进行的排水活动已将许多这些碳汇变成了温室气体排放源。恢复退化的湿地,特别是在泥炭丰富的地区,作为一种基于自然的缓解气候变化的解决方案正越来越受到推崇。然而,恢复的轨迹和时间仍然不确定,尤其是考虑到植被动态、水文和温室气体通量之间复杂的相互作用。在本研究中,我们分析了加利福尼亚州萨克拉门托 - 圣华金河三角洲恢复湿地的44个站点年的二氧化碳(CO)和甲烷(CH)通量的连续涡度协方差测量数据。我们的研究结果揭示了各站点温室气体交换存在显著的年际变化,这是由恢复设计、水管理和植被建立的差异所驱动的。虽然植被快速生长,特别是密集的大型植物群落,可以增强二氧化碳的吸收,但它往往会增加甲烷排放,并使预测湿地何时成为净温室气体汇变得复杂。至关重要的是,由于水位高或不稳定(例如,大幅水位下降)导致植被建立延迟的湿地,即使在恢复多年后仍持续作为温室气体排放源。相反,通过精心种植或自然且快速重新定殖的站点表现出更早向净汇状态的转变,包括自恢复以来更早向净负辐射强迫的转变。该研究强调了适应性的、因地制宜的恢复策略和长期监测对于捕捉从源到汇的转换动态的重要性。随着全球对湿地恢复的投资增加,我们的研究结果强调了在缓解气候目标与生态现实以及植被演替的自我设计过程之间取得平衡的必要性。