Department of Agriculture and Fisheries, Queensland Government, University of the Sunshine Coast, Sippy Downs 4556, Australia; Faculty of Science, Health, Education and Engineering, University of the Sunshine Coast, Sippy Downs 4556, Australia.
Faculty of Science, Health, Education and Engineering, University of the Sunshine Coast, Sippy Downs 4556, Australia.
Sci Total Environ. 2019 Feb 1;649:1502-1513. doi: 10.1016/j.scitotenv.2018.08.351. Epub 2018 Aug 29.
Tropical regions of the world experience high rates of land-use change and this has a major influence on terrestrial carbon (C) pools and the global C cycle. We assessed land-use change from agriculture to reforested plantings (with endemic species), up to 33 years of age, using 10 paired sites in the wet tropics, Australia. We determined the impacts on 0-50 cm below-ground C (soil organic C (SOC), charcoal C, humic organic C, particulate organic C, resistant organic C), C stored in roots (fine and coarse), C stored in living above-ground biomass and debris C pools. Reforested areas accumulated ecosystem C at a rate of 7.4 Mg ha yr. Reforestation plantings contained, on average, 2.3 times more ecosystem C than agricultural areas (102 Mg ha and 233 Mg ha, respectively). Most of the C accumulation was in living above-ground and below-ground biomass (60 and 30%, respectively) with a smaller amount in debris pools (16%). Apart from C in roots, soil C accumulation was not obvious across sites ranging from 8 to 33 years since reforestation, relative to the agricultural baseline. Differences in SOC (and associated SOC pools) to a depth of 50 cm, did exist between reforested areas and adjacent agriculture at some sites, however there was not a consistent trend in SOC associated with reforestation. Local site-based factors (e.g. soil texture and mineralogy, land-use history and microbial activity) appear to have a strong influence on the direction of the change in SOC. While reforestation in the tropics has great potential to accumulate C in biomass in living vegetation, and debris pools, it is likely to take approximately 50 years before C stocks of reforested areas resemble natural ecosystems. Accumulation of SOC through reforestation is difficult to achieve, highlighting the need to conserve carbon pools in remnant forests in the tropics.
世界热带地区经历了高土地利用变化率,这对陆地碳(C)库和全球碳循环有重大影响。我们在澳大利亚潮湿热带地区使用 10 对配对地点评估了从农业到再造林种植(含特有物种),年龄达 33 年的土地利用变化。我们确定了对 0-50cm 以下土壤 C(土壤有机 C(SOC)、木炭 C、腐殖质有机 C、颗粒有机 C、抗有机 C)、根系(细根和粗根)中储存的 C、活地上生物量和残体 C 库中储存的 C 的影响。重新造林区以每年 7.4Mg ha yr 的速度积累生态系统 C。重新造林种植区的生态系统 C 平均比农业区多 2.3 倍(分别为 102 Mg ha 和 233 Mg ha)。大部分 C 积累在活地上和地下生物量中(分别为 60%和 30%),残体库中积累的 C 较少(16%)。除了根系中的 C 之外,重新造林后 8 至 33 年的时间内,土壤 C 积累在各地点并不明显,相对于农业基线而言。在一些地点,重新造林区和相邻农业区之间的 SOC(和相关的 SOC 库)在 50cm 深度上存在差异,但与重新造林相关的 SOC 没有一致的趋势。基于地点的因素(例如土壤质地和矿物学、土地利用历史和微生物活性)似乎对 SOC 变化的方向有很大影响。虽然热带地区的再造林具有在活植被和残体库中积累 C 的巨大潜力,但重新造林区的 C 储量可能需要大约 50 年才能与自然生态系统相似。通过再造林积累 SOC 是困难的,这突显了保护热带地区剩余森林碳库的必要性。