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Arctic LTER Database

Acceptance and utilization of LTER data requires that:

(1) The Principal Investigator be sent a notice stating reasons for acquiring any data and a description of the publication intentions.
(2) The Principal Investigator of the data set be sent a copy of the report or manuscript prior to submission and be adequately cited in any resultant publications.
(3) A copy of any resultant publications should be sent to:

Principal Investigator
Ecosystems Center
Marine Biological Laboratory
7 MBL St.
Woods Hole, MA 02543

Older Metadata: Attribute table not in XML (EML) file

Dataset URLs:METADATA: HTML, Rich Text, XML(EML compliant)
DATA: Comma Delimited, Excel file with Metadata and data
Dataset ID:96boht04
Dataset Title:TRhodamine WT (RWT) concentrations with in the hyporheic and parafluvial zones of lower Kuparuk River as a result of a continuos addition of the conservative tracer, RWT, to the channel at an upstream site, Arctic LTER 1996.
Investigator 1: 
First Name:William
Last Name:Bowden
Address line 1:
Address line 2:
Address line 3:
City:
State:
Zip Code:
Country:
Associate Investigators:Kenneth Edwardson
Keywords:Kuparuk, hyporheic, Rhodamine WT, tracer, temperature, phosphate, nitrate, ammonium, dissolved oxygen, specific, conductivity, methane, and carbon dioxide
Abstract: TRhodamine WT (RWT) concentrations with in the hyporheic and parafluvial zones of lower Kuparuk River as a result of a continuos addition of the conservative tracer, RWT, to the channel at an upstream site. Additionally, the concentration of one or more of the following, associated with a given hyporheic at some time during the addition, exists within the file; phosphate, nitrate, ammonium, dissolved oxygen, specific conductivity, methane, and carbon dioxide.
Contact: Arctic LTER Information Manager
The Ecosystems Center
Marine Biological Lab
7 MBL St
Woods Hole, MA 02543
Phone (508) 289 7496
Email: arc_im@mbl.edu
Online URL: http://ecosystems.mbl.edu/ARC/
DATA FILE INFORMATION:
Data File Name 96boht04
Beginning Date 5/1/1996
End Date 9/1/1996
Number of Data Records
Other Files to Reference
Availability Status
Quality Control Information
Maintenance Description
Log of Changes: Log of changes: For Archival Use: DATA RECEIVED: June 1997 DATA FILE ENTERED BY: Karie Slavik DATA FILE VALIDATION: NAME: DATA:
RESEARCH LOCATION:
Geographic Description Near the mouth of the Kuparuk river in Prudhoe bay area (+1800meters) in conjunction with the 1996 15N addition.
Location Bounding Box
West Bounding Coordinate
East Bounding Coordinate
North Bounding Coordinate
South Bounding Coordinate
OR if single point location
Latitude
Longitude
TAXONOMIC COVERAGE:
Organisms studied
Methods:

Samplers were installed longitudinally down a riffle and down-
gradient along the left and right pointbars of the instrumented
riffle.
Well Construction/Installation: Hyporheic samplers consisted of
a 1/8 inch O.D. stainless steel (S.S.) tube housed in a 3/4 inch
CPVC pipe. At the lower end of the CPVC a rubber stopper was
inserted with the S.S tube protruding ten centimeters. A coupler
was then used to attach a length of well screen to protect the
S.S. tube. Tygon tubing was slid onto the top end of the S.S
tubing and a three-way Pharmaseal stopcock was inserted into the
tubing. Samplers were inserted into the stream bed by forcing a
pry bar into the stream bed to a depth of the maximum depth
allowed, typically 30-60 centimeters. The sampler was then
worked down into the hole and the pry bar removed, allowing the
hole to cave in onto the sampler. The length of the sampler,
still above the substrate, was measured and subtracted from the
total length to find the depth of the sampler in the substrate.
Samplers were allowed to settle before any testing occurred.
Sample collection: Samples were collected via a 60 mL syringe
directly from the sampler after drawing 30 mL out to purge the
interior of the sampler. Samples were places directly into a 13
mm diameter borsilicate glass vial with a Teflon lined cap that
could be placed directly into the fluorometer. Samples collected
for ammonium, nitrate and phosphate were immediatly filtered
through a 0.45 um cellulose acetate filter and stored cold until
analysis.
Sample analysis: Specific conductivity was measured in the field
on a VWR model 2052 conductivity meter. All sample analysis was
done within 24 hours of collection and stored cold during the
interim period. Ammonia-nitrogen concentrations were determined
by the phenate method. Nitrate-nitrogen was determined by
cadmium reduction. Phosphate-phosphorous was determined by the
ascorbic acid method. Samples were analyzed for their RWT
concentration on a Turner Designs model AU-10 fluorometer.
Carbon dioxide and methane were measured directly by
equilibration of the sample with ambient air. The head-space air
was then analyzed by thermal conductivity for CO2 and flame
ionization for CH4. Concentrations were corrected for ambient
concentrations, depth, temperature, and pH.

Notes: The variable, D/D for River distance is in
reference to the top of the riffle and the distances established
by the 1996, 15N addition. Use the X and Y coordinates (river
right to left and distance downstream) for more detailed
positions.
(12) VARIABLE DESCRIPTIONS:







Precision
Coded?
Missing
Variable
Variable Description
Units
(Y/N)
Values
Site

River






n
n
D/D

River distance


meters
n
n


Series
Sampler Location




n
y
Number
Sampler number





n
y
X

X-coordinate



meters
n
y
Y

Y-coordinate



meters
n
y
Time
Time





hhmm

n
y
Date

Date





dd-mmm-yy
n
n
RWT

Rhodamine WT concentration
ug/L

n
y
CO2

Carbon Dioxide



umoles/L
n
y
CH4

Methane




umoles/L
n
y
Depth
Depth of Sampler


cm

n
y
SPC

Conductivity



mmhos
n
y
NH4

Ammonia




umoles/L
n
y
PO4

Phosphate



umoles/L
n
y
NO3

Nitrate




umoles/L
n
y
Temp

Temperature



Celsius
n
y
Comments

Reference Citations: American Public Health Association. 1989. Standard methods for
the examination of water and wastewater. 17th ed. American
Public Health Association, American Water Works Association, and
Water Pollution Control Federation, Washington, DC.
Kling,G.W., Kipphut, G.W., and Miller, M.C. 1992. The Flux of
CO2 and CH4 from lakes and rivers in arctic Alaska.
Hydrobiologia, 240:23-36.

Sampling Description.

None

Data Table

Site		River							n	n
D/D		River distance 			meters	n	n		
Series	Sampler Location					n	y
Number	Sampler number						n	y
X		X-coordinate				meters	n	y
Y		Y-coordinate				meters	n	y
Time 	Time						hhmm		n	y
Date		Date						dd-mmm-yy	n	n
RWT		Rhodamine WT concentration	ug/L		n	y
CO2		Carbon Dioxide				umoles/L	n	y
CH4		Methane					umoles/L	n	y
Depth	Depth of Sampler			cm		n	y
SPC		Conductivity				mmhos	n	y
NH4		Ammonia					umoles/L	n	y
PO4 		Phosphate 				umoles/L	n	y
NO3		Nitrate 					umoles/L	n	y
Temp		Temperature				Celsius	n	y
Comments

Please contact arc_im@mbl.edu with questions, comments, or for technical assistance regarding this web site.