Biology Centre AS CR, Institute of Hydrobiology, Na Sádkách 7, 37005 České Budějovice, Czech Republic.
Biology Centre AS CR, Institute of Hydrobiology, Na Sádkách 7, 37005 České Budějovice, Czech Republic.
Sci Total Environ. 2014 Feb 1;470-471:543-50. doi: 10.1016/j.scitotenv.2013.10.013. Epub 2013 Oct 26.
Using dynamic, mass budget, and empirical models, we quantified sulphate-sulphur (SO4-S) leaching from soils in a large central European catchment (upper Vltava river, Czech Republic) over a 110-year period (1900-2010). SO4-S inputs to soils with synthetic fertilisers and atmospheric deposition increased in the 1950s-1980s, then rapidly decreased (~80%), and remained low since the middle 1990s. The proportion of drained agricultural land rapidly increased from 4 to 43% between the 1950s and 1990s; then the draining ability of the system slowly decreased due to its ageing. Sulphate concentrations in the Vltava exhibited similar trends as the external SO4-S inputs, suggesting that they could be explained by changes in atmospheric and fertiliser S inputs. The available data and modelling, however, showed that (i) internal SO4-S sources (mineralization of soil organic S in the drained agricultural land), (ii) a hysteresis in SO4-S leaching from forest soils (a net S retention at the high S inputs and then a net release at the lowered inputs), and (iii) hydrology must be taken into account. An empirical model was then employed, based on parameters representing hydrology (discharge), external SO4-S sources (inputs by synthetic fertilisers and atmospheric deposition), and internal SO4-S sources (mineralization related to soil drainage). The model explained 84% of the observed variability in annual SO4-S concentrations in the Vltava river during 1900-2010 and showed that forest soils were a net sink (105 kg ha(-1)) while agricultural land was a net source (55 kg ha(-1)) of SO4-S during 1960-2010. In the late 1980s, forest soils changed from a sink to a source of S, and the present release of SO4-S accumulated in forest soils thus delays recovery of surface waters from acidification, while S losses from agricultural soils increase the risk of future S deficiency in S-demanding crops.
利用动态、质量平衡和经验模型,我们量化了中欧一个大型流域(捷克共和国上易北河)土壤中硫酸盐-硫(SO4-S)在 110 年期间(1900-2010 年)的淋失情况。20 世纪 50 年代至 80 年代,随着合成肥料和大气沉降中 SO4-S 的输入增加,土壤中 SO4-S 的输入量迅速减少(约 80%),并自 20 世纪 90 年代中期以来一直保持在较低水平。20 世纪 50 年代至 90 年代,排水农业用地的比例从 4%迅速增加到 43%;随后,由于系统老化,排水能力逐渐下降。易北河中的硫酸盐浓度与大气和肥料 S 输入的外部 SO4-S 输入呈相似趋势,表明它们可以通过大气和肥料 S 输入的变化来解释。然而,现有数据和模型表明,(i)内部 SO4-S 来源(排水农业用地中土壤有机 S 的矿化),(ii)森林土壤中 SO4-S 淋失的滞后效应(高 S 输入时净 S 保留,然后低输入时净 S 释放),以及(iii)水文学必须考虑在内。然后,基于代表水文学(流量)、外部 SO4-S 来源(合成肥料和大气沉降输入)和内部 SO4-S 来源(与土壤排水相关的矿化)的参数,采用经验模型。该模型解释了 1900-2010 年易北河年 SO4-S 浓度观测变化的 84%,并表明森林土壤是 SO4-S 的净汇(105 kg ha(-1)),而农业用地是 SO4-S 的净源(55 kg ha(-1))在 1960-2010 年期间。20 世纪 80 年代末,森林土壤由 S 的汇转变为 S 的源,因此,目前在森林土壤中积累的 SO4-S 的释放会延迟地表水从酸化中恢复,而农业土壤中 S 的损失会增加对 S 需求作物未来 S 缺乏的风险。