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Modeling Acidification Recovery on Threatened Ecosystems: Application to the Evaluation of the Gothenburg Protocol in France

机译:在受威胁的生态系统上模拟酸化恢复:在法国哥德堡协议评估中的应用

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To evaluate the acid deposition reduction negotiated for 2010 within the UNECE LRTAP Gothenburg Protocol,sulphur and nitrogen deposition time-series (1880-2100) were compared to critical loads of acidity on five French ecosystems: Massif Central basalt (site 1) and granite (2);Paris Bassin tertiary sands (3);Vosges mountains sandstone (4) and Landes eolian sands (5).The SAFE model was used to estimate the response of soil solution pH and [Al]/[BC] ratio to the deposition scenario.Among the five sites,critical loads were exceeded in the past at sites 3,4 and 5.Sites 3 and 4 were still expected to exceed in 2010,the Protocol year.Further reduction of atmospheric deposition,mainly nitrogen,would be needed to achieve recovery on these ecosystems.At sites 3,4 and 5,the delay between the critical load exceedance and the violation of the critical chemical criterion was estimated to be 10 to 30 years in the top soil and 50 to 90 years in the deeper soil.At site 5,a recovery was expected in the top soil in 2010 with a time lag of 10 years.Unexpectedly,soil pH continued to decrease after 1980 in the deeper soil at sites 2 and 5.This time lag indicated that acidification moved down the soil profile as a consequence of slow base cation depletion by ion exchange.This delayed response of the soil solution was the result of the combination of weathering rates and vegetation uptake but also of the relative ratio between base cation deposition and acid compounds.
机译:为了评估在UNECE LRTAP哥德堡议定书中商定的2010年减少的酸沉降量,将硫和氮沉降的时间序列(1880-2100)与法国五个生态系统:Massif Central玄武岩(站点1)和花岗岩( 2);巴黎盆地三级砂(3);孚日山脉砂岩(4)和兰德斯风积砂(5)。使用SAFE模型估算土壤溶液pH和[Al] / [BC]比对沉积的响应在这五个站点中,过去在站点3、4和5超出了临界负荷。预计在议定书年2010年,站点3和4仍将超过临界负载。需要进一步减少大气沉积,主要是氮为了在这些生态系统上实现恢复。在地点3、4和5,超出临界负荷和违反临界化学标准之间的延迟时间估计在表层土壤中为10至30年,在深部土壤中为50至90年。土壤。在站点5,预计恢复表层土壤在2010年出现了10年的时间滞后。出乎意料的是,1980年之后,土壤深处2和5处的土壤pH值继续下降。该时间滞后表明,由于碱性阳离子耗竭缓慢,酸化作用沿土壤剖面下降土壤溶液的这种延迟响应是风化速率和植被吸收的结合,也是碱性阳离子沉积与酸化合物之间的相对比率的结果。

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