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首页> 外文期刊>Hydrology and Earth System Sciences >Modelling reversibility of central European mountain lakes from acidification: Part II - the Tatra Mountains
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Modelling reversibility of central European mountain lakes from acidification: Part II - the Tatra Mountains

机译:通过酸化模拟欧洲中部山区湖泊的可逆性:第二部分-塔特拉山

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摘要

A dynamic, process-based model of surface water acidification, MAGIC7. has been applied to four representative alpine lakes in the Tatra Mountains, (Slovakia and Poland). The model was calibrated for a set of 12 to 22-year experimental records of lake water composition. Surface water and soil chemistry were reconstructed front 1860 to 2002 and forecast to 2 050 based on the reduction in sulphur and nitrogen emissions presupposed by the Gothenburg Protocol. Relatively small changes in the soil C:N ratios were not sufficient to simulate observed changes in NO3- concentrations, so an alternative empirical approach of changes in terrestrial N uptake was applied. Measured sulphate sorption isotherms did not allow calibration of the pattern of sulphate response in the lakes, indicating that other mechanisms of S release were also important. The lake water chemistry exhibited significant changes during both the acidification advance (1860 to 1980s) and retreat (1980s to 2010). An increase in lake water concentrations of strong acid anions (SAA: 104-149 mueq l(-1)) was balanced by a decline in HCO3- (13-62 mueq l(-1)) and an increase in base cations (BC; 42-72 mueq l(-1)), H+ (0-18 mueq l(-1)) and Al-i(n+) (0-26 mueq l(-1)). The carbonate buffering system was depleted in three lakes. In contrast, lake water concentrations of SAA, BC, H+ and Al-i(n+) decreased by 57-82, 28-42. 0-11, and 0-22 mueq l(-1), respectively, the carbonate buffering system was re-established, and HCO3- increased by 1-21 mueq l(-1) during the chemical reversal from atmospheric acidification (by 2000). The MAGIC7 model forecasts a slight continuation in this reversal for the next decade and new steady-state conditions thereafter. Gran alkalinity should come back to 1950s levels (0-71 mueq l(-1)) in all lakes after 2010. Partial recovery of the soil pool of exchangeable base cations can be expected in one catchment, while only conservation of the current conditions is predicted for three lakes. Even though the pre-industrial alkalinity values of 16-80 mueq l(-1) will not be reached due to the insufficient recovery of soil quality, the ongoing chemical improvement of water should be sufficient for biological recovery of most alpine takes in the Tatra Mountains. [References: 44]
机译:动态的,基于过程的地表水酸化模型MAGIC7。已应用于塔特拉山(斯洛伐克和波兰)的四个有代表性的高山湖泊。针对一组12至22年的湖水成分实验记录对模型进行了校准。地表水和土壤化学在1860年之前重建到2002年,并根据《哥德堡议定书》预设的硫和氮排放量减少预测为2050。土壤C:N比的相对较小的变化不足以模拟观察到的NO3-浓度变化,因此采用了一种替代的经验性方法来改变陆地氮的吸收。测得的硫酸盐吸附等温线无法校准湖泊中硫酸盐响应的模式,这表明其他S释放机理也很重要。在酸化推进(1860年至1980年代)和退酸化(1980年代至2010年)期间,湖水化学都表现出显着变化。湖水中强酸阴离子(SAA:104-149 mueq l(-1))的浓度增加与HCO3-(13-62 mueq l(-1))的减少和碱性阳离子(BC)的增加相平衡;42-72μeql(-1)),H +(0-18μeql(-1))和Al-i(n +)(0-26μeql(-1))。碳酸盐缓冲系统在三个湖泊中枯竭。相反,湖水中SAA,BC,H +和Al-i(n +)的浓度分别降低了57-82、28-42。分别从0-11和0-22 mueq l(-1)重新建立碳酸盐缓冲系统,并且在从大气酸化的化学过程中(到2000年)HCO3-增加了1-21 mueq l(-1)。 )。 MAGIC7模型预测,在接下来的十年中,这种逆转将继续出现轻微的延续,此后又出现新的稳态条件。在2010年之后,所有湖泊的大粒碱度应恢复到1950年代的水平(0-71 mueq l(-1))。在一个流域中,可交换基础阳离子的土壤池有望部分恢复,而目前的保护条件是预测为三个湖泊。即使由于土壤质量恢复不足而无法达到工业化前的16-80 mueq l(-1)碱度,正在进行的水化学改良也应足以对塔特拉地区的大多数高山生物进行生物恢复山。 [参考:44]

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