Daniel Ruane , Jay Martin , Michael Brooker , Blanca Bernal , Chris Anderson , Robert Nairn , William J. Mitsch
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While long-term carbon sequestration rates for natural wetlands are well-documented, it is unknown how constructed wetlands sequester carbon long-term. The Olentangy River Wetland Research Park (ORWRP) in Columbus, Ohio, USA is an ideal location to research this due to its extensive datasets collected over 29 years of biogeochemical and ecological monitoring. We used soil core samples taken across two constructed freshwater wetlands to quantify carbon storages and paired this data with similar studies at 18-month, 10-year, and 15-year milestones to create a timeline of carbon sequestration across 29 years. Our findings suggest that both wetlands have sequestered relatively equal amounts of carbon since construction and neither have shown a net gain or loss since year 15. At year 29, the average carbon storage between both wetlands is 3.58 ± 2.21 kg C m<sup>−2</sup> which equates to 0.12 ± 0.08 kg C m<sup>−2</sup> yr<sup>−1</sup>, which is similar to other constructed wetlands. 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引用次数: 0
摘要
国际气候变化专门委员会(IPCC)已明确表示,为了防止全球变暖达到 1.5 ℃ 的灾难性水平,必须减少碳排放和促进碳固存。IPCC 将对 "高碳生态系统 "的投资确定为一项潜在的减缓战略,湿地就是其中之一。从历史上看,世界上大部分湿地都因人类活动而遭到破坏,美国中西部是受影响最严重的地区之一。直到最近,美国才试图通过强制建设湿地来取代被排干的湿地,以弥补这一损失。虽然天然湿地的长期碳固存率有据可查,但建造的湿地如何长期固碳却不得而知。位于美国俄亥俄州哥伦布市的奥伦坦吉河湿地研究园(ORWRP)是研究这一问题的理想地点,因为它在 29 年的生物地球化学和生态监测过程中收集了大量数据集。我们利用在两块建造好的淡水湿地上采集的土壤核心样本来量化碳储存量,并将这些数据与 18 个月、10 年和 15 年里程碑上的类似研究配对,以创建 29 年来的碳固存时间表。我们的研究结果表明,自建成以来,两处湿地的碳螯合量相对相当,且自第 15 年以来均未出现净增或净减。在第 29 年,两块湿地的平均碳储量为 3.58 ± 2.21 kg C m-2,相当于 0.12 ± 0.08 kg C m-2 yr-1,与其他人工湿地相似。结果表明,这些湿地很可能已达到稳定状态,在当前条件下,预计未来不会出现碳增减。由于这些湿地和其他人工湿地的固碳率高于其他耕地改造方案,因此它们代表了一种成功的气候变化减缓策略。
29 years of carbon sequestration in two constructed riverine wetlands
The International Panel on Climate Change (IPCC) has made it clear that a reduction in carbon emissions and a promotion in carbon sequestration are necessary in order to prevent the planet from reaching catastrophic warming levels of 1.5 °C globally. The IPCC identifies the investment in “high‑carbon ecosystems” as a potential mitigation strategy, with one such ecosystem being wetlands. Historically, the majority of the world's wetlands have been destroyed due to human activities, with the midwestern U.S. being one of the most affected regions. Only in recent history has the U.S. sought to remedy this by mandating the construction of wetlands to replace those that are drained. While long-term carbon sequestration rates for natural wetlands are well-documented, it is unknown how constructed wetlands sequester carbon long-term. The Olentangy River Wetland Research Park (ORWRP) in Columbus, Ohio, USA is an ideal location to research this due to its extensive datasets collected over 29 years of biogeochemical and ecological monitoring. We used soil core samples taken across two constructed freshwater wetlands to quantify carbon storages and paired this data with similar studies at 18-month, 10-year, and 15-year milestones to create a timeline of carbon sequestration across 29 years. Our findings suggest that both wetlands have sequestered relatively equal amounts of carbon since construction and neither have shown a net gain or loss since year 15. At year 29, the average carbon storage between both wetlands is 3.58 ± 2.21 kg C m−2 which equates to 0.12 ± 0.08 kg C m−2 yr−1, which is similar to other constructed wetlands. Results indicate that these wetlands likely have reached stability and are not expected to exhibit future carbon gains or losses under current conditions. Because these and other constructed wetlands have greater carbon sequestration rates than other options for conversion of croplands, they represent a successful climate change mitigation strategy.
期刊介绍:
Ecological engineering has been defined as the design of ecosystems for the mutual benefit of humans and nature. The journal is meant for ecologists who, because of their research interests or occupation, are involved in designing, monitoring, or restoring ecosystems, and can serve as a bridge between ecologists and engineers.
Specific topics covered in the journal include: habitat reconstruction; ecotechnology; synthetic ecology; bioengineering; restoration ecology; ecology conservation; ecosystem rehabilitation; stream and river restoration; reclamation ecology; non-renewable resource conservation. Descriptions of specific applications of ecological engineering are acceptable only when situated within context of adding novelty to current research and emphasizing ecosystem restoration. We do not accept purely descriptive reports on ecosystem structures (such as vegetation surveys), purely physical assessment of materials that can be used for ecological restoration, small-model studies carried out in the laboratory or greenhouse with artificial (waste)water or crop studies, or case studies on conventional wastewater treatment and eutrophication that do not offer an ecosystem restoration approach within the paper.