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                <gco:CharacterString>Samples were collected in the lower reaches of Von Guerard stream in January 2019 along a transect P2 as reported by Heindel et al. 2021. Sediment sampling methods, metadata, and information regarding total extractable ammonium and additional ancillary data are also reported by&#160;Heindel et al. 2021.&#160;We utilized subsamples from the P2 (pool morphology) transect. Wet sediment subsamples were weighed in triplicate for each sampling location (1-5) into sterile 250 mL HDPE wide mouth bottles and kept frozen (-20 ºC) prior to running the assay. For the assay, we prepared five solutions of varying conductivities using potassium chloride. The specific conductivity of each treatment solution was measured using a benchtop probe and a three or four point calibration. Sediment samples were removed from the freezer and treatment solution was added to each bottle to achieve a 2:5 sediment:solution ratio by mass. Bottles were inverted three times and placed on a shaker table at 300 rpm for 1 hour. Slurries were centrifuged at 3000 rpm for 5 minutes and then the supernatant was filtered through glass fiber filters (GF/F) and stored frozen prior to analysis. Supernatant aliquots were analyzed by the Arikaree Environmental Laboratory at the University of Colorado Boulder. Potassium was measured by Method EPA 7000B on a Perkin Elmer Model AAnalyst 200 Atomic Absorption Spectrometer with a limit of detection of 0.004 mg K+ per liter. Chloride was measured by Method EPA 300.1 on a Metrohm 930 Compact IC Flex with a limit of detection of 0.03 mg Cl- per liter. Nitrogen as ammonium measured by Method 10-107-06-1-A on a Lachat Quickchem Flow Injection Autoanalyzer with a limit of detection of 0.005 mg N per liter. Nitrogen as nitrate plus nitrite measured by Methods 10-107-04-1-A and 10-117-07-1-B on a Lachat Quickchem Flow Injection Autoanalyzer with a limit of detection of 0.002 mg N per liter.</gco:CharacterString>
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