4.4 Article

Phosphorus sorption characteristics and interactions with leaf litter-derived dissolved organic matter leachate in iron-rich sediments of a sub-tropical ephemeral stream

期刊

AQUATIC SCIENCES
卷 84, 期 4, 页码 -

出版社

SPRINGER BASEL AG
DOI: 10.1007/s00027-022-00888-x

关键词

Ephemeral stream; Fluorescence spectroscopy; Groundwater; High molecular weight organic carbon; Hematite; Sorption kinetics

资金

  1. ARC [LP120200002]
  2. Rio Tinto (RTIO)
  3. Rangelands NRM Western Australia
  4. CAUL
  5. Australian Research Council [LP120200002] Funding Source: Australian Research Council

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This study investigated the influence of dissolved organic matter (DOM) additions on the phosphate sorption kinetics of iron-rich sediments. The results showed that low-dose DOM addition reduced sediment P adsorption capacity, while high-dose DOM addition increased it. The study also revealed that phosphorus availability in dryland streams can be modulated by varying the concentration of humic-rich DOM.
This study investigated the influence of dissolved organic matter (DOM) additions on phosphate sorption kinetics of iron-rich sediments (39-50% hematite and goethite) from an ephemeral stream in the arid Pilbara region of sub-tropical northwest Australia. While phosphate sorption in stream sediments is known to be strongly influenced by sediment mineralogy as well as interactions with DOM, the mechanisms and significance of DOM on P-release from sediments with high sorption capacities, are largely undescribed. We assessed phosphorus (P) sorption behaviours by adding a range of solutions of known inorganic P concentrations that were amended with variable loadings of DOM derived from leachates of leaf litter to sediments from stream pools during the non-flowing phase. We compared the sorption capacity of the sediments and concurrent changes in DOM composition measured using fluorescence spectroscopy. We show that the low-dose DOM addition (similar to 4 mg L-1 DOC) had the effect of reducing sediment P adsorption capacity, while for the high-dose DOM addition (similar to 45 mg L-1 DOC), it was increased. The high-dose DOM was similar to pore water DOC and likely saturated sediment surface adsorption sites and produced P-OM-Fe complexes. This resulted in increased removal of P from solution. Sediment P sorption characteristics were well fitted to both Freundlich and Langmuir isotherm models regardless of DOC concentration. Langmuir P sorption maxima ranged from 0.106 to 0.152 mg g(-1). General P sorption characteristics of these iron-rich sediments did not differ among pools of contrasting hydrological connectivity. Our results show how humic-rich DOM can modulate the sediment P availability in dryland streams. Unravelling the complexities of P availability is of particular significance to further our understanding of biogeochemical processes in aquatic ecosystems where P often acts as a limiting nutrient.

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