1996
DOI: 10.1007/bf02150537
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Changes in Al and Fe crystallinity and P sorption capacity in a flood-plain forest soil subjected to artificially manipulated flooding regimes in field mesocosms

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Cited by 15 publications
(6 citation statements)
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“…In contrast, de Vicente et al (2010) found an apparently non-reversible decrease of amorphous Fe oxides during oxic rewetting of dried lake sediment (no change of Al Ox ) resulting in a reduced P sorption capacity and an increased P release. The reversibility of the occurred crystallization of Al Ox (in our experiment) is in agreement with decreases in crystallinity of Al and Fe in floodplain forest soils (Darke et al, 1997;Darke & Walbridge, 2000) and is important for the evaluation of the sustainable effect of drying on sediment properties (Baldwin, 1996).…”
Section: Simulation Of Drying and Rewetting With Intact Sediment Coressupporting
confidence: 73%
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“…In contrast, de Vicente et al (2010) found an apparently non-reversible decrease of amorphous Fe oxides during oxic rewetting of dried lake sediment (no change of Al Ox ) resulting in a reduced P sorption capacity and an increased P release. The reversibility of the occurred crystallization of Al Ox (in our experiment) is in agreement with decreases in crystallinity of Al and Fe in floodplain forest soils (Darke et al, 1997;Darke & Walbridge, 2000) and is important for the evaluation of the sustainable effect of drying on sediment properties (Baldwin, 1996).…”
Section: Simulation Of Drying and Rewetting With Intact Sediment Coressupporting
confidence: 73%
“…The effect of rewetting on the degree of crystallinity of Fe and aluminum (Al) forms is very contradictory described in the literature. Both a decrease (Sah et al, 1989;Darke et al, 1997;Darke & Walbridge, 2000) as well as an, apparently non-reversible, increase [of Fe oxides (de Vicente et al, 2010)] were observed and resulted in the latter case in a reduced P sorption capacity and an increased P release.…”
Section: Introductionmentioning
confidence: 89%
“…In general, the variations in transformations of phosphorus among different landscape characteristics (such as geology) are not as well studied as abundance and transport. Individual studies have described phosphorus transformations in different watersheds with distinct mineralogies [e.g., Darke et al, 1996;Litaor et al, 2003;Lapworth et al, 2011]; evaluated the correlation of phosphorus with abundance of phosphorus binding compounds or other soil characteristics [e.g., Vanek, 1993;Evans et al, 2000;Prior and Johnes, 2002]; or (in a few cases) proposed conceptual models of the effects of redox level gradients on phosphorus release, or of landscape-scale hydrologic characteristics on the development of redox conditions or an index-based susceptibility to phosphorus loss [e.g., Hill, 2000;Reid et al, 2012].…”
Section: Transformationmentioning
confidence: 99%
“…Environmental phosphorus models may not include dynamics that have proven to be important controls of river corridor phosphorus in field studies (e.g., only some models simulate different sorption rates for calcareous and non-calcareous soils, although lab studies show there is marked difference between the two) [Darke et al, 1996;McGechan and Lewis, 2002;Havlin et al, 2005;Robson, 2014].…”
Section: Introductionmentioning
confidence: 99%
“…While the main channel and deeper parts of floodplain backwaters remain permanently inundated, riparian zones and shallow areas are periodically falling dry and get re-wetted depending on their topography and the surface flow paths. Water level fluctuations and desiccation are expected to have a strong effect on internal phosphorus loading by altering redox conditions of sediments, pH, physical properties of minerals ( Aldous et al, 2005; Baldwin, 1996; Baldwin and Mitchell, 2000; Darke et al, 1996; Lijklema, 1980; Sah et al, 1989 ) and the composition and activity of the microbial community ( Batzer and Sharitz, 2006 ).…”
Section: Introductionmentioning
confidence: 99%