2018
DOI: 10.1002/2017gb005677
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Contribution of Hydrologic Opportunity and Biogeochemical Reactivity to the Variability of Nutrient Retention in River Networks

Abstract: In‐stream nutrient retention results from the interaction between hydrological and biogeochemical processes involved in downstream transport. While hydrological processes set the opportunity for nutrient retention to occur, metabolic activity and abiotic processes determine the potential biogeochemical reactivity of streams. Yet, a comprehensive assessment of the relevance of hydrological opportunity versus biogeochemical reactivity on the variability of nutrient retention across streams is still missing. We c… Show more

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Cited by 49 publications
(34 citation statements)
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“…However, the % nutrient retention is the outcome of both hydraulics as well as biogeochemical reactivity. The factors influencing biogeochemical reactivity, such as NO 3 and organic carbon supply, temperature, or hyporheic flow path do change from headwaters to large rivers [7,62] and have been found to be more important for N retention variability than previously thought [63]. Hence, the high biogeochemical reactivity of the Elbe may also explain the comparably high % retention rates found here.…”
Section: N-retention Efficiency In Large Riverssupporting
confidence: 44%
“…However, the % nutrient retention is the outcome of both hydraulics as well as biogeochemical reactivity. The factors influencing biogeochemical reactivity, such as NO 3 and organic carbon supply, temperature, or hyporheic flow path do change from headwaters to large rivers [7,62] and have been found to be more important for N retention variability than previously thought [63]. Hence, the high biogeochemical reactivity of the Elbe may also explain the comparably high % retention rates found here.…”
Section: N-retention Efficiency In Large Riverssupporting
confidence: 44%
“…Other potentially important factors include variation of river network structure, flow regimes, the effect of disturbance, loading distributions (in space and time), seasonality of process rates, internal aquatic sources, role of water column processes, and their interactions. All these factors can differ among watersheds and among biomes (Mineau et al 2015;Ruegg et al 2016;Helton et al 2017;Marcé et al 2018;Park et al 2018;Gardner and Doyle 2018).…”
Section: Implications Of the Rnsmentioning
confidence: 99%
“…Previous work examining the watershed patch size at which variance collapse occurs found smaller extent patches (3–61 km 2 ) for labile constituents and larger extent patches (113–216 km 2 ) for conservative constituents (Abbott et al, 2018; Shogren et al, 2019), which correspond with second‐ to third‐order watersheds in the Kuskokwim (47–208 km 2 ). For labile nutrients like PO 4 3− and NO 3 − , this pattern of variance collapse is likely due to some combination of higher cumulative uptake with distance downstream and shorter residence times in larger channels (Ensign & Doyle, 2006; Marcé et al, 2018; Mulholland et al, 2009), in addition to the expected spatial averaging that occurs as small tributaries combine into larger streams. Variance collapse in [DOC] has been attributed to net gains of allochthonous instream organic matter inputs along the network (Shogren et al, 2019).…”
Section: Discussionmentioning
confidence: 99%