the Creative Commons Attribution 4.0 License.
the Creative Commons Attribution 4.0 License.
Phosphorus attenuation in streams by water-column geochemistry and benthic sediment reactive iron
Abstract. Streams can attenuate inputs of phosphorus (P) and, therefore the likelihood of ecosystem eutrophication. This attenuation is, however, poorly understood, particularly in reference to the geochemical mechanisms involved. In our study, we measured P attenuation mechanisms in the form of (1) mineral (co-)precipitation from the water-column and (2) P sorption with benthic sediments. We hypothesized that both mechanisms would vary with catchment geology and, further, that P sorption would depend on reactive Fe content in sediments. We sampled 31 streams at baseflow conditions, covering a gradient of P inputs (via land use), hydrological characteristics, and catchment geologies. Geochemical equilibria in the water-column were measured and benthic sediments (< 2 mm) were analyzed for sorption properties and P and iron (Fe) fractions. Neither P-containing minerals (e.g., hydroxylapatite) nor calcite-phosphate co-precipitation had the potential to occur. In contrast, in-stream dissolved reactive P (DRP) correlated with labile sediment P (water-soluble and easily reduced Fe-P), but only for streams where hyporheic exchange between the water-column and the coarse sediment porewaters was likely sufficient. The non-labile P fractions contained most of sediment P (generally > 90 %) and varied with parent geology. Similarly, most sediment Fe was in a recalcitrant form (generally > 90–95 %). However, despite its small contribution to total sediment Fe, the pool of surface-reactive Fe was a strong predictor for sediment P sorption potential. Our results suggest that, in these streams, it is the combination of biogeochemical Fe and P cycles and the exchange with the hyporheic zone that attenuates DRP in baseflow. Such combinations are likely to vary spatiotemporally within a catchment and must be considered alongside inputs of P and sediment if the P concentrations at baseflow – and eutrophication risk – are to be well managed.
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RC1: 'Review of Manuscript bg-2019-400', Anonymous Referee #1, 26 Nov 2019
- AC1: 'Authors' response to Reviewers #1 and #2', Zachary Simpson, 16 Jan 2020
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RC2: 'Review of bg-2019-400', Anonymous Referee #2, 09 Dec 2019
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AC1: 'Authors' response to Reviewers #1 and #2', Zachary Simpson, 16 Jan 2020
- AC2: 'Rejoinder of major revisions for referee #2's comments', Zachary Simpson, 18 Mar 2020
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AC1: 'Authors' response to Reviewers #1 and #2', Zachary Simpson, 16 Jan 2020
-
RC1: 'Review of Manuscript bg-2019-400', Anonymous Referee #1, 26 Nov 2019
- AC1: 'Authors' response to Reviewers #1 and #2', Zachary Simpson, 16 Jan 2020
-
RC2: 'Review of bg-2019-400', Anonymous Referee #2, 09 Dec 2019
-
AC1: 'Authors' response to Reviewers #1 and #2', Zachary Simpson, 16 Jan 2020
- AC2: 'Rejoinder of major revisions for referee #2's comments', Zachary Simpson, 18 Mar 2020
-
AC1: 'Authors' response to Reviewers #1 and #2', Zachary Simpson, 16 Jan 2020
Data sets
Sediment survey data Z. Simpson https://doi.org/10.6084/m9.figshare.9630722
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Cited
2 citations as recorded by crossref.
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- Use of Geomatic Techniques for Mapping Suspended Solids in Aquatic Ecosystems: The Case Study of Guayas River, Ecuador J. Yepez Ramírez et al. 10.48084/etasr.8664