Impact of Re-wetting of Forestry-Drained Peatlands on Water Quality—a Laboratory Approach Assessing the Release of P, N, Fe, and Dissolved Organic Carbon

被引:0
作者
Annu Kaila
Zaki Asam
Markku Koskinen
Risto Uusitalo
Aino Smolander
Oili Kiikkilä
Sakari Sarkkola
Connie O’Driscoll
Veikko Kitunen
Hannu Fritze
Hannu Nousiainen
Arja Tervahauta
Liwen Xiao
Mika Nieminen
机构
[1] Natural Resources Institute Finland,Department of Civil Engineering
[2] National University of Ireland Galway,Department of Environmental Sciences
[3] University of Gujrat,Department of Forest Sciences
[4] University of Helsinki,Department of Civil
[5] National Resources Institute Finland,undefined
[6] Trinity College Dublin,undefined
[7] Structural and Environmental Engineering,undefined
[8] Museum Building,undefined
[9] Trinity College,undefined
来源
Water, Air, & Soil Pollution | 2016年 / 227卷
关键词
DOC; Iron; Peatland forests; Phosphorus; Nitrogen; Restoration;
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摘要
A laboratory column study with peats from four sites from south-central Finland and two sites from blanket peats in the west of Ireland was established to assess the factors contributing to P, N, Fe, and dissolved organic carbon (DOC) transfer to receiving water courses from restored forestry-drained peatlands. The study indicated that the DOC and Fe release from re-wetted peats are likely governed by the amount of Fe in peat and the degree of Fe reduction upon re-wetting. In contrast to our other hypothesis concerning DOC, high degradability of organic matter was not related to high DOC release. Nitrate release was found to largely cease along with oxygen depletion, but ammonium release was considerable from a site with high nitrification potential before wetting. The release of P from anoxic peat was complicated in the sense that it appeared to be controlled by many factors simultaneously. In the nutrient-poor sites, the P release increased following re-wetting, probably because of their high easily soluble peat P content and low Al and Fe content, resulting in high anoxic P mobilization, but limited re-sorption of the mobilized P. Among the three nutrient-rich sites, there was either no P release upon re-wetting or higher P release than from the nutrient-poor sites. Low risk for P release following re-wetting in nutrient-rich sites was associated with low content in peat of easily soluble P and a high molar Fe/P ratio.
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