Central Chemical Laboratory, Leibniz-Institute of Freshwater Ecology and Inland Fisheries, Müggelseedamm 301, D-12587 Berlin, Germany.
Ecol Appl. 2010 Jul;20(5):1336-49. doi: 10.1890/08-2053.1.
Rewetting of drained fens is necessary to stop further soil degradation and to reestablish important ecological functions. However, substantial changes of peat characteristics in the upper soil layers, due to drainage and land use, could counteract their recovery as nutrient-poor systems for an unknown period. We assessed the importance of altered peat properties, such as the degree of peat decomposition and the amount of redox-sensitive phosphorus (P) compounds, for P mobilization in different degraded fens. An experimental design involving 63 intact peat cores from fens with varying drainage and land-use histories was developed to quantify the mobilization of P, as well as that of iron (Fe), ammonium, carbon dioxide, and methane, all indicators of organic-matter decomposition and/or P-releasing processes. We found that net P release rates in peat cores with highly decomposed peat (range: 0.1-52.3 mg P x m(-2) x d(-1)) were significantly correlated to the amount of P bound to redox-sensitive compounds and the molar Fe:P as well as Al:P ratios of peat. We conclude that the following general rules apply for P mobilization in rewetted fens: (1) elevated levels of P release rates and P concentrations in pore water up to three orders of magnitude larger than under natural reference conditions can only be expected for rewetted fens whose surface soil layers consist of highly decomposed peat; (2) peat characteristics, such as the amount of P bound to redox-sensitive Fe(III) compounds (positive correlation) and molar ratios of Fe:P or Al:P (negative correlations), explain the high range of P release rates; and (3) a critical P export to adjacent lakes or rivers can only be expected if molar Fe:P ratios of highly decomposed peat are less than 10.
排干的沼泽湿地需要重新湿润,以阻止进一步的土壤退化并重新建立重要的生态功能。然而,由于排水和土地利用,上层土壤中泥炭特性的重大变化可能会在未知的时间内抵消其作为贫营养系统的恢复。我们评估了改变的泥炭特性的重要性,例如泥炭分解的程度和氧化还原敏感磷(P)化合物的数量,对于不同退化沼泽湿地中 P 的迁移。设计了一个涉及 63 个来自具有不同排水和土地利用历史的沼泽湿地的完整泥炭芯的实验设计,以量化 P 的迁移,以及铁(Fe)、铵、二氧化碳和甲烷的迁移,所有这些都是有机物质分解和/或释放过程的指标。我们发现,高度分解的泥炭(范围:0.1-52.3mg P x m(-2) x d(-1))中泥炭芯的净 P 释放率与与氧化还原敏感化合物结合的 P 量以及泥炭的摩尔 Fe:P 和 Al:P 比值显著相关。我们得出结论,以下一般规则适用于再湿润沼泽湿地中 P 的迁移:(1) 只有在表面土壤层由高度分解的泥炭组成的再湿润沼泽湿地中,才能预期到高达三个数量级的孔隙水中 P 释放率和 P 浓度的升高,超过自然参考条件;(2) 泥炭特性,如与氧化还原敏感 Fe(III)化合物结合的 P 量(正相关)和摩尔比的 Fe:P 或 Al:P(负相关),解释了 P 释放率的高范围;(3) 只有当高度分解的泥炭的摩尔 Fe:P 比值小于 10 时,才能预期到向相邻湖泊或河流的临界 P 输出。