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CAS Workshop on Ecosystem Succession Theory and Practice of Ecological Restoration 

Effects of reforestation, afforestation and harvest on forest ecosystem carbon cycling: Managing forests to mitigate climate change

 Pan Yude  Richard Birdsey

(USDA Forest Service, Global Change Program, Newtown Square, PA 19073, USA)

 Abstract: The UNFCCC was negotiated with the aim of reducing fossil fuel emissions because of the likely climate effects of increasing CO2 concentrations. Aside from limiting fossil fuel consumption, the protocol includes provisions for managing natural terrestrial carbon sinks, primarily afforestation and reforestation, to increase sink strength and reduce atmospheric CO2. Thus, understanding the nature of terrestrial carbon sinks, their distribution, control, longevity, and reliability is an increasing demand for both the scientific community and government agencies. 

Forest ecosystems play dominant roles in the carbon cycle because they store a large amount of C in vegetation and soil, and interact with atmospheric processes through the absorption and respiration of CO2. Recent research has highlighted the role of the Northern Hemisphere as a carbon sink and suggested that the mid-latitude forests were likely the primary places where carbon sequestration has been enhanced. There is no doubt that forest ecosystems can be managed to reduce carbon emission and increase carbon sink size significantly; yet there are different opinions about how to manage forests to increase sinks. The Kyoto Protocol manages young forest stands because of their greater capacity for assimilating carbon. However, some scientists suggest that preservation of natural old growth forests may have larger effects on the carbon cycle than promotion of regrowth because harvesting may cause short-term losses of ecosystem carbon. According to the Kyoto Protocol, carbon sources and sinks from the Kyoto forests that consist of post-1990 reforestation, afforestation and deforestation can be counted as a country’s efforts to reduce emission. Replacement of old-growth forests by young Kyoto stands can gain the credit as part of forest management.

Many studies have suggested that reforestation and afforestation could be an effective way to sequester carbon. Field data and the simulation results of the succession model TEM-LPJ illustrated that annual NPP in forest stands was likely to reach the maximal at ages between 20 and 30 and then decline before level off.  The carbon storage in forest vegetation could saturate as forests aged over 50 years old. One of our recent studies on China forest carbon estimation indicated that the carbon pool in China forest trees had increased approximately 13% since early 1970s, reflecting the impact of reforestation and afforestation programs in China since the 1960s. Our results showed that the carbon sequestration rate from the late 1980s to the early 1990s was significantly higher, which was likely related to the change of age structure in China forests that reached more productive stages. In this study, we compared forest carbon estimates of China, the conterminous U.S., and Russia for the period of 1988-1993. The results further showed the effect of ages on forest carbon sequestration. Although China had much less forested lands and a smaller forest carbon pool than the U.S. and Russia, the area-weighted C sequestration rate was highest because of younger forests and greater C sequestration capacity. 

The criticism of the forest management strategy under the Kyoto Protocol is that the protocol is not based on a full ecosystem carbon budget including all ecosystem components and applies only to specific “commitment” periods instead of a long time period. It is argued that the carbon budget of forests is determined more by respiration than assimilation.  In forest ecosystems, most carbon is stored in pools such as wood, litter and soil organic matter that differ in their turnover time ranging from daily to millennium timescales. About two thirds of terrestrial carbon is stored in soils and generally has slower turnover rates than aboveground carbon. Without disturbances, soil organic carbon in passive pools can be maintained over longer period of time.

The studies of forest ecosystems revealed that large carbon losses could take place after a stand harvest because of tremendous increase of respiratory and leaching losses. A full harvest resets the vegetation to an early stage of succession. TEM-LPJ simulated soil carbon dynamic in a secondary succession of a stand in Harvard Forest after an assumed clear cutting. The soil carbon pools appeared to decline for several years because the litter input of the regrowth was lower than the decay rate of organic matter already present in the soil. The modeled results of secondary succession indicated that it took 60-80 years for soil carbon pools to recover to the precutting level in forest sites, which agreed with experimental results at Harvard Forest. The raised concern is that the forest management credited by the Kyoto protocol, such as reforesting old-growth forests, may lead to massive carbon losses by reducing passive soil carbon pools and create an incentive for actions that can actually increase cumulative emission. Thus, net biome production (NBP), a new concept that represents a full carbon budget over sufficient time scales to reflect changes in long-term carbon storage, is suggested as an appropriate basis for any accounting system for terrestrial carbon regarding the development of C emission restriction in the Kyoto protocol. 

Because of large uncertainties in calculating carbon budget associated with land-use change and forestry, it requires our better understanding about regulation processes of terrestrial carbon balance across scales from plots to continents and from daily to millennium. For forest ecosystems, statistically accurate estimates for aboveground change of carbon storage are readily available, but the estimates for belowground components are poor and uncertain. We lack knowledge for verifying soil carbon changes in the past decades attributed to land-use changes and disturbances. Nowadays, the impacts of human-induced disturbances have become such a prominent property of all ecosystems that affects carbon fluxes at all spatial and temporal scales. Our recent research indicated that changed atmospheric chemistry such as CO2 concentration and N deposition not only affected forest sequestration capacity, also altered allocation pattern of carbon to different pools of forest ecosystems.

We should understand that managing forest ecosystems to reduce carbon emission only serves as a temporary solution because a substantial fraction of the fossil fuel carbon sequestered in terrestrial sinks is vulnerable to return to the atmosphere on time scale from decades to century. Terrestrial sinks are thus best viewed as buying valuable time to reduce industrial emissions. Although many processes that influence the net terrestrial sink are beyond direct human management, careful evaluation and adoption of appropriate strategy for managing forest ecosystems, especially enhancing sizes of stable carbon pools, are certainly important for achieving our goals to mitigate climate change. 

Key words: Carbon sequestration; Kyoto Protocol; forest management; deforestation/afforestation; full harvest; net biome production (NBP); climate change

 

作者简介:潘愉德,女,1957年生,纽约州立大学植物生态学博士,现工作于美国农业部森林服务局(USDA Forest Service),俄亥俄州托利多大学兼职教授,USDA亚太项目主管、美国生态学会亚洲生态学部秘书。研究领域包括全球变化、生态系统生态学、碳循环、生物地球化学循环、生态系统模型等。研究项目包括美国农业部的森林碳素研究、中国森林碳储量与积累、森林服务与森林健康监测、全球变化对区域的影响评价、基于过程的生态系统模型整合、美国宇航局的碳研究计划、中华海外生态学者协会(SINO-ECO2000-2002届主席。发表论文50多篇。Email: ypan@fs.fed.us

 

 

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