Wageningen University and Research, Environmental Research (Alterra), PO Box 47, NL-6700 AA Wageningen, The Netherlands; Wageningen University and Research, Environmental Systems Analysis Group, PO Box 47, NL-6700 AA Wageningen, The Netherlands.
Coordination Centre for Effects (CCE), RIVM, PO Box 1, NL-3720 BA Bilthoven, The Netherlands.
Sci Total Environ. 2017 Dec 15;605-606:1097-1116. doi: 10.1016/j.scitotenv.2017.06.132. Epub 2017 Jul 19.
We modelled the effects of past and expected future changes in climate (temperature, precipitation), CO concentration, nitrogen deposition (N) and ozone (O) exposure (phytotoxic ozone dose, POD) on carbon (C) sequestration by European forest ecosystems for the period 1900-2050. Tree C sequestration was assessed by using empirical response functions, while soil C sequestration was simulated with the process-based model VSD, combined with the RothC model. We evaluated two empirical growth responses to N deposition (linear and non-linear) and two O exposure relationships (linear function with total biomass or net annual increment). We further investigated an 'interactive model' with interactions between drivers and a 'multiplicative model', in which the combined effect is the product of individual drivers. A single deposition and climate scenario was used for the period 1900-2050. Contrary to expectations, growth observations at European level for the period 1950-2010 compared better with predictions by the multiplicative model than with the interactive model. This coincides with the fact that carbon responses in kgChayr per unit change in drivers, i.e. per °C, ppm CO, kgNhayr and mmolmyr POD, are more in line with literature data when using the multiplicative model. Compared to 1900, the estimated European average total C sequestration in both forests and forest soils between 1950 and 2000 increased by 21% in the interactive model and by 41% in the multiplicative model, but observed changes were even higher. This growth increase is expected to decline between 2000 and 2050. The simulated changes between 1950 and 2000 were mainly due to the increase in both N deposition and CO, while the predicted increases between 2000 and 2050 were mainly caused by the increase in CO and temperature, and to lesser extent a decrease in POD, counteracted by reduced N deposition.
我们模拟了过去和预期未来的气候变化(温度、降水)、CO 浓度、氮沉降(N)和臭氧(O)暴露(植物毒性臭氧剂量,POD)对欧洲森林生态系统 1900-2050 年碳(C)固存的影响。通过使用经验响应函数评估树木 C 固存,而通过基于过程的模型 VSD 结合 RothC 模型模拟土壤 C 固存。我们评估了两种对 N 沉降的经验生长响应(线性和非线性)和两种 O 暴露关系(与总生物量或净年增量的线性函数)。我们进一步研究了一个具有驱动因素相互作用的“交互模型”和一个“乘法模型”,其中组合效应是各个驱动因素的乘积。在 1900-2050 年期间,我们使用单一的沉积和气候情景。与预期相反,1950-2010 年期间欧洲水平的生长观测结果与乘法模型的预测相比,与交互模型的预测相比更好。这与以下事实相符,即当使用乘法模型时,单位驱动因素变化(即每°C、ppm CO、kgNhayr 和 mmolmyr POD)的碳响应更符合文献数据。与 1900 年相比,在交互模型中,1950 年至 2000 年间森林和森林土壤的欧洲平均总 C 固存量增加了 21%,在乘法模型中增加了 41%,但观测到的变化甚至更高。这种增长的增加预计将在 2000 年至 2050 年之间下降。1950 年至 2000 年之间的模拟变化主要归因于 N 沉降和 CO 的增加,而 2000 年至 2050 年之间的预测增加主要归因于 CO 和温度的增加,以及在一定程度上 POD 的减少,这被减少的 N 沉降所抵消。