Checking for non-preferred file/folder path names (may take a long time depending on the number of files/folders) ...

AIMS Paint Rock Field Discharge Data (AIMS_SE_PRF_DISL)


Authors:
Owners: This resource does not have an owner who is an active HydroShare user. Contact CUAHSI (help@cuahsi.org) to determine if accessing this resource is possible.
Type: Resource
Storage: The size of this resource is 128.7 KB
Created: Jun 20, 2025 at 4:38 p.m. (UTC)
Last updated: Jul 23, 2025 at 12:02 a.m. (UTC)
Citation: See how to cite this resource
Sharing Status: Private (Accessible via direct link sharing)
Views: 31
Downloads: 0
+1 Votes: Be the first one to 
 this.
Comments: No comments (yet)

Abstract

This study was conducted in the Paint Rock research watershed (outlet location: 34.96861724, -86.16501705) on privately owned property in Jackson County (AL, USA). The watershed drains a non-perennial unnamed tributary to Burks Creek, and contains 2.97 km^2 of deciduous forest in the Cumberland Plateau physiographic section. Located near Estillfork, AL, the watershed spans an elevation range from 211 to 550 m above sea level, and is a tributary to the Paint Rock River (within the larger Tennessee basin). The region has a humid subtropical climate, with mean daily January and July air temperatures of 4.4°C and 25.4°C respectively, and mean annual precipitation of 1,390 mm/yr. These samples were collected in support of the core sampling goals of the Aquatic Intermittency effects on Microbiomes in Streams (AIMS) Project. Between 13 October 2021 and 6 June 2024, we conducted pulse additions of NaCl (i.e., "salt slugs") to estimate discharge (Q; liters per second) and velocity (v; meters per second) at the watershed outlet (TLM01) every 3 weeks during routine sensor maintenance (AIMS Approach 1) and seasonally at seven distributed, long term monitoring sites (AIMS Approach 2).

Briefly, discharge and velocity were estimated by adding a known mass of NaCl dissolved in approximately 1 liter of stream water to an upstream "addition" site and measuring changes in conductivity using a Solinst Conductivity Sensor (at 2 second intervals) at a downstream "logging" site. Discharge (in liters per second) was estimated using the mass of salt added and the area under the background conductivity-corrected "breakthrough curve" (e.g., change in conductivity over time at the logging site from the arrival of the salt tracer until conductivity returns to pre-salt slug background levels). Velocity (in meters per second) was estimated using nominal travel time (time for 50% of salt mass to pass the logging site) and the reach length between the addition and logging site. Salt slugs were only conducted if the reach upstream of the sample site was fully connected and flowing continuously for a distance of at least ten wetted widths. For R scripts and individual tracer breakthrough curves used to estimate discharge and travel time, please contact Stephen Plont (plontste@gmail.com)

Subject Keywords

Coverage

Spatial

Coordinate System/Geographic Projection:
WGS 84 EPSG:4326
Coordinate Units:
Decimal degrees
Longitude
-86.1646°
Latitude
34.9705°

Temporal

Start Date:
End Date:

Content

Related Resources

Credits

Funding Agencies

This resource was created using funding from the following sources:
Agency Name Award Title Award Number
U.S. National Science Foundation Aquatic Intermittency Effects of Microbiomes on Streams 2019603

How to Cite

Plont, S., D. Peterson, N. Jones, S. Speir (2025). AIMS Paint Rock Field Discharge Data (AIMS_SE_PRF_DISL), HydroShare, http://www.hydroshare.org/resource/d52b989e537349019842dba236627b66

This resource is shared under the Creative Commons Attribution CC BY.

http://creativecommons.org/licenses/by/4.0/
CC-BY

Comments

There are currently no comments

New Comment

required