Home > Publications database > Land use and soil factors affecting accumulation of phosphorus species in temperate soils > print |
001 | 203170 | ||
005 | 20210129220312.0 | ||
024 | 7 | _ | |2 doi |a 10.1016/j.geoderma.2015.03.020 |
024 | 7 | _ | |2 ISSN |a 0016-7061 |
024 | 7 | _ | |2 ISSN |a 1872-6259 |
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100 | 1 | _ | |0 P:(DE-HGF)0 |a Stutter, Marc I. |b 0 |e Corresponding author |
245 | _ | _ | |a Land use and soil factors affecting accumulation of phosphorus species in temperate soils |
260 | _ | _ | |a Amsterdam [u.a.] |b Elsevier Science |c 2015 |
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520 | _ | _ | |a Data on the distribution of phosphorus (P) species in soils with differing land uses and properties are essential to understanding environmental P availability and how fertiliser inputs, cropping and grazing affect accumulation of soil inorganic P (Pi) and organic P (Po) forms. We examined thirty-two temperate soils (with soil organic C concentrations 12–449 g C kg− 1 and total P 295–3435 mg P kg− 1) for biogeochemical properties of soil C, reactive surfaces and P by common indices and 31P-NMR spectroscopy on NaOH–EDTA extracts for P species. Arable soil P was dominated by inorganic orthophosphate (276–2520 mg P kg− 1), > monoester P (105–446 mg P kg− 1). The limited diesters, polyphosphates and microbial P in arable soils suggest that cropping and fertiliser inputs limit ecosystem microbial functions and P diversity. Intensive grassland had inorganic orthophosphate concentrations (233–842 mg P kg− 1) similar to monoesters (200–658 mg P kg− 1) > diesters (0–50 mg P kg− 1) and polyphosphates (1–78 mg P kg− 1). As grazing became more extensive P in semi-natural systems was dominated by organic P, including monoesters (37–621 mg P kg− 1) and other diverse forms; principally diester (0–102 mg P kg− 1) and polyphosphates (0–108 mg P kg− 1). These were related to SOC, water extractable organic carbon (WEOC) and microbial P, suggesting strong microbially-mediated processes. A number of abiotic and biotic related processes appeared to control accumulation of different soil P species and gave considerable variability in forms and concentrations within land use groups. The implications are that to increase agricultural P efficiencies mechanisms to utilise both soil Pi and Po are needed and that specific management strategies may be required for site-specific circumstances of soil C and reactive properties such as Fe and Al complexes. |
536 | _ | _ | |0 G:(DE-HGF)POF3-255 |a 255 - Terrestrial Systems: From Observation to Prediction (POF3-255) |c POF3-255 |f POF III |x 0 |
588 | _ | _ | |a Dataset connected to CrossRef |
700 | 1 | _ | |0 P:(DE-HGF)0 |a Shand, Charles A. |b 1 |
700 | 1 | _ | |0 P:(DE-HGF)0 |a George, Timothy S. |b 2 |
700 | 1 | _ | |0 P:(DE-HGF)0 |a Blackwell, Martin S. A. |b 3 |
700 | 1 | _ | |0 P:(DE-HGF)0 |a Dixon, Liz |b 4 |
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700 | 1 | _ | |0 P:(DE-HGF)0 |a MacKay, Regina L. |b 6 |
700 | 1 | _ | |0 P:(DE-HGF)0 |a Richardson, Alan E. |b 7 |
700 | 1 | _ | |0 P:(DE-HGF)0 |a Condron, Leo M. |b 8 |
700 | 1 | _ | |0 P:(DE-HGF)0 |a Haygarth, Philip M. |b 9 |
773 | _ | _ | |0 PERI:(DE-600)2001729-7 |a 10.1016/j.geoderma.2015.03.020 |g Vol. 257-258, p. 29 - 39 |p 29 - 39 |t Geoderma |v 257-258 |x 0016-7061 |y 2015 |
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