Data Package Metadata   View Summary

Ecosystem metabolism and associated environmental data for a forested, meadow and reforested reach of White Clay Creek, Chester Co., Pennsylvania; 1971-1975 and 1997-2010

General Information
Data Package:
Local Identifier:edi.1417.8
Title:Ecosystem metabolism and associated environmental data for a forested, meadow and reforested reach of White Clay Creek, Chester Co., Pennsylvania; 1971-1975 and 1997-2010
Alternate Identifier:DOI PLACE HOLDER
Abstract:

Ecosystem metabolism data for a 3rd-order Piedmont stream were collected during two periods: P1- April 1971 – Dec 1975, and P2- May 1997 – January 2010. Measures were made in a meadow and a forested reach during each period and in a reforested (formerly meadow) reach during the latter years of P2. During P1, measures were made by transferring streambed substrata to chambers in water jackets located on the streambank and measuring dissolved oxygen changes over diel periods. During P2, open system measures of dissolved O2 change were made for several days in warm and cold seasons, with reaeration determined from a propane injection experiment. Metabolism estimates were determined from diel curves of dissolved O2 change. Photosynthetically active radiation (PAR) and chlorophyll were measured concurrent with many measurements in P1 and all measures during P2, and temperature with all measures. Water chemistry parameters (NH4-N, NO3-N, PO4-P, SiO2, Cl, SO4, total alkalinity, pH) associated with each run are included in the data set, as are days since storm of various thresholds.

Field procedures, analytical methods and data analyses are detailed in Bott, T.L. & J. D. Newbold, 2023. A multi-year analysis of factors affecting ecosystem metabolism in forested and meadow reaches of a Piedmont Stream. Hydrobiologia

Publication Date:2023-05-15
For more information:
Visit: DOI PLACE HOLDER

Time Period
Begin:
1971-04-07
End:
2010-01-21

People and Organizations
Contact:Bott, Thomas L. (Stroud Water Research Center, Research Scientist Emeritus) [  email ]
Creator:Bott, Thomas L. (Stroud Water Research Center)
Creator:Montgomery, David (Stroud Water Research Center)
Creator:Newbold, J. Denis (Stroud Water Research Center)
Creator:Ritter, Floyd (Stroud Water Research Center)
Associate:Newbold, J.  Denis (Stroud Water Research Center, Conservative tracer modeling, data analysis)
Associate:Ritter, Floyd (Stroud Water Research Center, Field work (P1), sensor maintenance, laboratory analyses, data preparation)
Associate:Pierson, Jean (Stroud Water Research Center, Chemical analyses (P1))
Associate:Dunn, Cindy (Stroud Water Research Center, Data analysis (P1))
Associate:Montgomery, David (Stroud Water Research Center, Field work (P2), sensor maintenance, laboratory analyses, data analysis)
Associate:Wallace, Bruce (Stroud Water Research Center, Field work (P2), sensor maintenance, laboratory analyses)
Associate:Colburn, Chad (Stroud Water Research Center, Field work (P2), sensor maintenance, laboratory analyses)
Associate:Parsons, Nancy (Stroud Water Research Center, Field work (P2))
Associate:Hughes, Brian (Stroud Water Research Center, Chlorophyll sample analysis (P2))
Associate:Gentile, Michael (Stroud Water Research Center, Chemical analyses (P2))
Associate:Roberts, Sherman (Stroud Water Research Center, Chemical analyses (P2))
Associate:Arnold, Melanie (Stroud Water Research Center, Data analysis (P2))
Associate:Fox, Robert (Stroud Water Research Center, Data analysis (P2))
Associate:Zwilling, Erica (Stroud Water Research Center, Data analysis (P2))
Associate:Dow, Charles L. (Stroud Water Research Center, Data analysis (P1 and P2))
Associate:Brooks, Heather (Stroud Water Research Center, Data analysis (P2))
Associate:Smith, Timothy (Stroud Water Research Center, Data analysis (P2))

Data Entities
Data Table Name:
Data_w group no_for EDI_09May23
Description:
Ecosystem metabolism and associated environmental data for a forested, meadow and reforested reach of White Clay Creek, Chester Co., Pennsylvania; 1971-1975 and 1997-2010.
Detailed Metadata

Data Entities


Data Table

Data:https://pasta-s.lternet.edu/package/data/eml/edi/1417/8/882f679b0ee77221f0924229196e691d
Name:Data_w group no_for EDI_09May23
Description:Ecosystem metabolism and associated environmental data for a forested, meadow and reforested reach of White Clay Creek, Chester Co., Pennsylvania; 1971-1975 and 1997-2010.
Number of Records:582
Number of Columns:34

Table Structure
Object Name:Data_w group no_for EDI_09May23_csv.csv
Size:120088 byte
Authentication:5d484253140a263d1e0def72d4003837 Calculated By MD5
Text Format:
Number of Header Lines:1
Record Delimiter:\r\n
Orientation:column
Simple Delimited:
Field Delimiter:,
Quote Character:"

Table Column Descriptions
 ReachDatePeriodCalendar season% Boulder, Cobble, Pebble% Clay + silt + sand% CanopySeason (cold or warm)Reclassify cold to warm for 2Way ANOVAGW Corrected M2 dataGPP (g O2.m-2.d-1)R24 (g O2.m-2.d-1)NDM_gO2.m_2.d_1P/RMean (mean Chlor a) (mg/m2)Mean Temp (°C)min Temp. (°C)Max. Temp. (°C)all daily PAR (mol quanta photons.m-2.day-1)pHNH4-N (mg/L)NO3-N (mg/L)PO4-P (mg/L)SiO2 (mg/L)Cl (mg/L)SO4 (mg/L)all TA (mg CaCO3/L)Mean daily flow (m3/s) Max. daily flowDays since storm threshold ≥ 2.8 m3/sDays since storm threshold ≥ 2.0 m3/sDays since storm threshold ≥ 1.2 m3/sDays since storm threshold ≥ 0.70 m3/sDays since storm threshold ≥ 0.30 m3/s
Column Name:Reach  
Date  
Period  
CalendarSeason  
P_BoulderCobblePebble  
P_ClaySiltSand  
P_Canopy  
Season3_CW  
Reclassify_CW_for2WayANOVA  
GWCorrectedM2Data  
GPP_gO2.m_2.d_1  
CR24prER24_gO2.m_2.d_1  
NDM_gO2.m_2.d_1  
P_R  
MeanChlorA_mgm2  
MeanTemp_C  
MinTemp_C  
MaxTemp_C  
AllDailyPAR_molquantaphotons_m_2.day_1  
pH  
NH4N_mgL  
NO3N_mgL  
PO4P_mgL  
SiO2_mgL  
Cl_mgL  
SO4_mgL  
allTA_mgCaCO3L  
MeanDailyFlow_m3s  
MaxDailyFlow_m3s  
DaysSinceStormThreshold_gte2.8m3s  
DaysSinceStormThreshold_gte2.0m3s  
DaysSinceStormThreshold_gte1.2m3s  
DaysSinceStormThreshold_gte0.70m3s  
DaysSinceStormThreshold_gte0.30m3s  
Definition:Stream reach type - forested, meadow, reforestedDate of collectionStudy period - 1 or 2Season of samplePercent of sample containing boulders, cobbles, or pebblesPercent of sample containing clay, silt and sandPercent of sample covered by canopyCategorized as cold or warm with temperature cutoff of ...Some cold/warm categories were reclassified if appropriate for a grouping - y indicates it was reclassifiedMeadow data corrected for groundwater intrusion - Y indicates yesGross primary productivityRespiration over 24 hoursNet daily metabolism (equivalent to net ecosystem productivity): NDM = GPP - R24Ratio of GPP to R24Mean chlorophyll A content in sampleMean temperature in degrees CelsiusMinimum temperature in degrees Celsius Maximum temperature in degrees CelsiusDaily Photosynthetically Active Radiation (PAR)pH of waterNH4-N content in sampleNO3-N content in samplePO4-P content in sampleSiO2 content in sampleCl content in sampleSO4 content in sampleTotal AlkalinityMean daily flow at sample locationMaximum daily flow at sample locationDays since a storm with a flow of greater than or equal to 2.8 cubic meters per second was reachedDays since a storm with a flow of greater than or equal to 2.0 cubic meters per second was reachedDays since a storm with a flow of greater than or equal to 1.2 cubic meters per second was reachedDays since a storm with a flow of greater than or equal to 0.70 cubic meters per second was reachedDays since a storm with a flow of greater than or equal to 0.30 cubic meters per second was reached
Storage Type:string  
dateTime  
string  
string  
float  
float  
float  
string  
string  
string  
float  
float  
float  
float  
float  
float  
float  
float  
float  
float  
float  
float  
float  
float  
float  
float  
float  
float  
float  
float  
float  
float  
float  
float  
Measurement Type:nominaldateTimenominalnominalratioratiorationominalnominalnominalratioratioratioratioratioratioratioratioratioratioratioratioratioratioratioratioratioratioratioratioratioratioratioratio
Measurement Values Domain:
Allowed Values and Definitions
Enumerated Domain 
Code Definition
CodeForested
DefinitionForested reach of stream
Source
Code Definition
CodeMeadow
DefinitionMeadow reach of stream
Source
Code Definition
CodeReforested
DefinitionReforested meadow reach of stream
Source
FormatYYYY-MM-DD
Precision
Allowed Values and Definitions
Enumerated Domain 
Code Definition
Code1
DefinitionPeriod lasting from April 1971 to December 1975
Source
Code Definition
Code2
DefinitionPeriod lasting from May 1997 to January 2010
Source
Allowed Values and Definitions
Enumerated Domain 
Code Definition
CodeSp
DefinitionSpring
Source
Code Definition
CodeSu
DefinitionSummer
Source
Code Definition
CodeAu
DefinitionAutumn
Source
Code Definition
CodeWi
DefinitionWinter
Source
Unitpercent
Typereal
Unitpercent
Typereal
Unitpercent
Typereal
Allowed Values and Definitions
Enumerated Domain 
Code Definition
Codenan
DefinitionMissing
Source
Code Definition
Codec
DefinitionCold <12 degrees C
Source
Code Definition
Codew
DefinitionWarm >=12 degrees C
Source
Allowed Values and Definitions
Enumerated Domain 
Code Definition
Codenan
DefinitionNo
Source
Code Definition
Codey
DefinitionYes (was reclassified from cold to warm or vice versa)
Source
Allowed Values and Definitions
Enumerated Domain 
Code Definition
Codenan
DefinitionNo
Source
Code Definition
CodeY
DefinitionYes (M2 data was corrected)
Source
UnitGramsOxygenPerMeterSquaredPerDay
Typereal
UnitGramsOxygenPerMeterSquaredPerDay
Typereal
UnitGramsOxygenPerMeterSquaredPerDay
Typereal
UnitUnitless
Typereal
UnitmilligramPerMeterSquared
Typereal
Unitcelsius
Typereal
Unitcelsius
Typereal
Unitcelsius
Typereal
UnitMolQuantaPhotonPerMeterSquaredPerDay
Typereal
UnitLogUnits
Typereal
UnitmilligramPerLiter
Typereal
UnitmilligramPerLiter
Typereal
UnitmilligramPerLiter
Typereal
UnitmilligramPerLiter
Typereal
UnitmilligramPerLiter
Typereal
UnitmilligramPerLiter
Typereal
UnitMilligramCaCO3PerLiter
Typereal
UnitmeterCubedPerSecond
Typereal
UnitmeterCubedPerSecond
Typereal
UnitDays
Typereal
UnitDays
Typereal
UnitDays
Typereal
UnitDays
Typereal
UnitDays
Typereal
Missing Value Code:        
Code.
ExplMissing
Code.
ExplMissing
Code.
ExplMissing
CodeNA
ExplMissing
CodeNA
ExplMissing
CodeNA
ExplMissing
Code.
ExplMissing
Code.
ExplMissing
Code.
ExplMissing
Code.
ExplMissing
Code.
ExplMissing
Code.
ExplMissing
Code.
ExplMissing
Code.
ExplMissing
Code.
ExplMissing
             
Code.
ExplMissing
Code.
ExplMissing
Code.
ExplMissing
Code.
ExplMissing
Code.
ExplMissing
Code.
ExplMissing
Code.
ExplMissing
Code.
ExplMissing
Accuracy Report:                                                                    
Accuracy Assessment:                                                                    
Coverage:                                                                    
Methods:                                                                    

Data Package Usage Rights

This information is released under the Creative Commons license - Attribution - CC BY (https://creativecommons.org/licenses/by/4.0/). The consumer of these data ("Data User" herein) is required to cite it appropriately in any publication that results from its use. The Data User should realize that these data may be actively used by others for ongoing research and that coordination may be necessary to prevent duplicate publication. The Data User is urged to contact the authors of these data if any questions about methodology or results occur. Where appropriate, the Data User is encouraged to consider collaboration or co-authorship with the authors. The Data User should realize that misinterpretation of data may occur if used out of context of the original study. While substantial efforts are made to ensure the accuracy of data and associated documentation, complete accuracy of data sets cannot be guaranteed. All data are made available "as is." The Data User should be aware, however, that data are updated periodically and it is the responsibility of the Data User to check for new versions of the data. The data authors and the repository where these data were obtained shall not be liable for damages resulting from any use or misinterpretation of the data. Thank you.

Keywords

By Thesaurus:
(No thesaurus)ecosystem metabolism, riparian reforestation, White Clay Creek, Stroud Water Research Center
LTER Controlled Vocabularyecosystem respiration, gross primary production, streams, stream ecology

Methods and Protocols

These methods, instrumentation and/or protocols apply to all data in this dataset:

Methods and protocols used in the collection of this data package
Description:

Metabolism data collection:

Metabolism estimates were based on changes in dissolved O2 measured over 24 h periods. In P1, trays of streambed substrata (337 cm2, 5 cm deep, 60 per reach) were incubated in situ. Metabolism measures were made on from 1 to 3 days per week by transferring one or more trays to clear acrylic chambers (22 L; 68.5 cm long x 30.5 cm wide x 14 cm deep) equipped for water recirculation (Teel Model IP598 submersible pumps, Dayton Electric, Chicago, IL). The chambers were located in water jackets on the streambank supplied with stream water to maintain near-ambient water temperature. After sealing the chamber, dissolved O2 concentrations were measured with a Model 60 flow-through probe (previously calibrated to Winkler dissolved O2 determinations) inserted in the recirculation line coupled with a Model 300 meter (Rexnord, Malvern, PA) and recorded on a strip chart recorder (Speed-o-Max M, Leeds and Northrop, North Wales, PA). To prevent O2 supersaturation as needed, the water jacket was covered with black plastic for 1 h and data for the preceding and succeeding hours were averaged and substituted for the hour the chamber was covered as data were processed. At the end of each run (beginning in September 1972), from 4 to 10 periphyton samples (10.2 cm2 x 0.5 cm deep) were scraped or cored from substrata for chlorophyll a determination and trays were returned to the stream for continued incubation. From one to three chambers were used per day. Chambers were scrubbed between use and recirculation lines were changed and boiled in water each week.

In P2 metabolism was measured in situ for 3 – 11 days during warm and cold seasons using open-system methodology. Model 600XL sondes (YSI, Inc., Yellow Springs, OH) coupled with a CR-500 data logger (Campbell Scientific, Logan, UT) in weatherproof housing (Rapid Creek Research, Boise, ID) or YSI Model 600XLM sondes with internal logging capability were used for continuous dissolved O2 monitoring. Probes were calibrated in water-saturated air and a sonde was positioned at the up- and down-stream end of each reach. Dissolved O2 and temperature data were logged every 15 min for up to 11 days. Reaeration was determined from a propane injection (Marzolf et al. 1994, 1998, Young & Huryn 1998) with bromide as a conservative tracer (Bott et al., 2006b), or from geomorphic and hydraulic variables (Owens et al., 1964; Tsivoglou & Neal, 1976) in seven cases. Quality control checks included incubation of sondes at a single location before and after each measurement series and, starting in 2000, daily checks of probe performance using an additional sonde and meter.

Instrument(s):Teel Model IP598 submersible pumps (Dayton Electric, Chicago, IL) Model 300 meter (Rexnord, Malvern, PA) Strip chart recorder (Speed-o-Max M, Leeds and Northrop, North Wales, PA) Model 600XL sondes (YSI, Inc., Yellow Springs, OH) CR-500 data logger (Campbell Scientific, Logan, UT)
Description:

Metabolism data analysis:

Diel rate-of-change curves were created from hourly changes in dissolved O2 (24 values per day in P1, 96 values per day in P2; Bott, 2006). Rate of change in dissolved O2 during pre-dawn and post-sunset hours were averaged and the mean multiplied by 24h to obtain a daily respiration rate (R24). Net change of dissolved O2 during the photoperiod was determined and respiration during the photoperiod added to that value to obtain gross primary productivity (GPP). Net daily metabolism (NDM = GPP – R24; alternatively, net ecosystem productivity) and the P/R ratio (GPP/R24) were computed. Data from days with more than one chamber measurement in P1 were averaged, first for riffle or pool habitat, and then over habitat, to generate estimates of reach metabolism.

For P2, the 2-station analytical procedure (Bott 2006, after Owens, 1974) was used except where data quality precluded its use, in which case the single station approach using data from the downstream sonde was applied (approx. one-third of the data sets). Night and day were differentiated by a PAR value of 2 µmol quanta photons.m-2.s-1 was used to differentiate night and day except when a higher value was needed to account for bright moonlight. Groundwater augmented flow within the Meadow 2 reach in January and February. GPP and R24 were corrected (McCutchan et al., 2002; Hall & Tank, 2005) using groundwater dissolved O2 measured in two nearby wells (8.60 mg.L-1).

Description:

Environmental data measurements:

Flow data were obtained from a continuously recording gauging station located ~ 60 m downstream from the bottom of the Meadow reach in P1 or from bromide dilution measured during propane injections in P2.

Water temperature was monitored using a Taylor thermograph (P1) or thermistors on the YSI sondes (P2).

Light was measured as total solar radiation during P1 and as above-water photosynthetically active radiation (PAR) during P2. A recording pyranometer (Model 8-48, Eppley, Newport, RI) located in near the Meadow reach and a recording pyroheliometer (Model 5-3850, Belfort Instruments, Baltimore, MD) installed at the Forested reach in September 1973 were used in P1. In P2, a quantum sensor (Model 190, LI-COR, Lincoln, NB) located mid-stream at each the end of the reach and data were logged to LI-COR Model 1400 data loggers.

Total solar radiation data for P1 were converted to an approximation of PAR by regressing PAR (mol quanta photons.m-2.d-1) against total radiation (“Energy” expressed as Mjoules.m-2.d-1) using data obtained by simultaneously monitoring total solar radiation and PAR with LI-COR sensors, Model 200-SA pyranometer and Model 190 quantum, respectively. For the Meadow, the equation used was: PAR = 1.933 Energy (R2 = 0.99, n=14 days). Two regressions were used for the Forested reach. The first (PAR = 1.83 Energy (R2 = 0.98, n=9 days) was applied to data collected between November 1 and May 9. It was based on data ranging from 1.5 to 9.2 MJoules.m-2.d-1collected in a greenhouse under neutral density screening. The other (PAR = 1.30 Energy, R2 = 0.90) was applied to data collected for the rest of the year when trees were leafed out and selective removal of photosynthetically active wavelengths occurred. It was based on data collected over 52 days in mid-summer with PAR sensors and an Eppley pyranometer moved sequentially to five locations under the forest canopy.

Chlorophyll samples were extracted overnight in buffered acetone in the dark at ≤4° C. Chlorophyll a was determined spectrophotometrically (Lorenzen, 1967). For P1, reach averaged estimates were produced as detailed for metabolism data. For P2, sample collection prior to 2000 followed Bott et al. (2006b). From 2000 on, periphyton cover types amounting to ≥ 10% of those seen through a viewing bucket at 200 locations in the reach (10 lateral points on 20 transects) were sampled and processed as described in Bott et al. (2006a) and analyzed as in P1. Chlorophyll estimates per m2 for each cover type were weighted for the proportion of the reach with that cover type and summed for a reach estimate.

Water chemistry was monitored at approximately weekly intervals. NH4+ was determined using the phenol –hypochlorite procedure (Solorzano, 1969) and the phenate procedure (EPA method 350.1) in P1 and P2, respectively; NO3- by chromotropic acid procedure (Am. Public Health Assoc. [APHA], 1971) in P1 and the cadmium reduction technique (EPA method 353.2) in P2; total alkalinity by methyl orange titration in P1 (APHA 1971) and Gran titration in P2 (EPA Method 310.1); and the following analyses during both periods: SiO2 (EPA method 370.1), SO42+ (EPA method 375.4), Cl- (EPA method 325.3) and PO43- (EPA method 365.1). EPA methods are found in U.S. EPA (1993). Cations were determined by atomic absorption spectrometry during P1 and by EPA method 200.7 during P2. pH was measured with a meter.

Days since storm of indicated thresholds were determined by counting back from the day of measurement to the day of storm of the indicated size.

Instrument(s):Model 600XL sondes (YSI, Inc., Yellow Springs, OH) Recording pyranometer (Model 8-48, Eppley, Newport, RI) Recording pyroheliometer (Model 5-3850, Belfort Instruments, Baltimore, MD) Quantum sensor (Model 190, LI-COR, Lincoln, NB)
Description:

For more information: field procedures, analytical methods and data analyses are detailed in Bott, T.L. & J.

D. Newbold, 2023. A multi-year analysis of factors affecting ecosystem metabolism in forested and meadow reaches of a Piedmont Stream. Hydrobiologia

Description:

Bibliography for Method Steps:

American Public Health Association [APHA], 1971. Standard methods for the examination of water and wastewater. American Public Health Association, New York.

Bott, T. L, 2006. Primary productivity and community respiration. In: Hauer, F. R. & G. A. Lamberti (eds), Methods in Stream Ecology, 2nd ed. Elsevier, Amsterdam: 663-690.

Bott, T. L., D. S. Montgomery, J. D. Newbold, D. B. Arscott, C. L. Dow, A. K. Aufdenkampe, J. K. Jackson & L. A. Kaplan, 2006a. Ecosystem metabolism in streams of the Catskill Mountains (Delaware and Hudson River watersheds) and Lower Hudson Valley. Journal of the North American Benthological Society 25: 1018 - 1044.

Bott, T. L., J. D. Newbold & D. B. Arscott, 2006b. Ecosystem metabolism in Piedmont streams: Reach geomorphology modulates the influence of riparian vegetation. Ecosystems 9: 398-421.

Hall, R. O., Jr. & J. L. Tank, 2005. Correcting whole-stream estimates of metabolism for groundwater inputs. Limnology and Oceanography Methods 3: 222-229.

Lorenzen, C. J., 1967. Determination of chlorophyll and pheopigments: Spectrophotometric equations. Limnology and Oceanography 12: 343-346.

Marzolf, E. R., P. J. Mulholland & A. J. Steinman, 1994. Improvements to the diurnal upstream-downstream dissolved oxygen change technique for determining whole-stream metabolism in small streams. Canadian Journal of Fisheries and Aquatic Sciences 51: 1591-1599.

Marzolf, E. R., P. J. Mulholland & A. J. Steinman, 1998. Reply: improvements to the diurnal upstream-downstream dissolved oxygen change technique for determining whole-stream metabolism in small streams. Canadian Journal of Fisheries and Aquatic Sciences 55: 1786-1787.

McCutchan, J. H., Jr., J. F. Saunders III, W. M. Lewis, Jr. & M. G. Hayden, 2002. Effects of groundwater flux on open-channel estimates of stream metabolism. Limnology and Oceanography 47: 321-324.

Owens, M., 1974. Measurements on non-isolated natural communities in running waters. In: Vollenweider, R. A. (ed), A Manual on Methods for Measuring Primary Production in Aquatic Environments. IPB Handbook 12, 2nd ed. Blackwell, Oxford: 111-119.

Owens, M., R. W. Edwards & J. W. Gibbs, 1964. Some reaeration studies in streams. International Journal of Air and Water Pollution 8: 469-486.

Solorzano, L., 1969. Determination of ammonia in natural waters by the phenolhypochlorite method. Limnology and Oceanography 14: 799-801.

Tsivoglou, H. C. & L. A. Neal, 1976. Tracer measurement of reaeration: III. Predicting the reaeration capacity of inland streams. Journal of the Water Pollution Control Federation 489: 2669-2689.

U.S. Environmental Protection Agency [US EPA], 1993. Determination of inorganic substances in environmental samples. EPA-600/R-93-100.

Young, R. G. & A. D. Huryn, 1998. Comment: improvements to the diurnal upstream-downstream dissolved oxygen change technique for determining whole-stream metabolism in small streams. Canadian Journal of Fisheries and Aquatic Sciences 55: 1784-1785.

People and Organizations

Publishers:
Organization:Environmental Data Initiative
Email Address:
info@edirepository.org
Web Address:
https://edirepository.org
Id:https://ror.org/0330j0z60
Creators:
Individual:Dr. Thomas L. Bott
Organization:Stroud Water Research Center
Email Address:
tlbott@stroudcenter.org
Individual: David Montgomery
Organization:Stroud Water Research Center
Individual:Dr. J. Denis Newbold
Organization:Stroud Water Research Center
Individual: Floyd Ritter
Organization:Stroud Water Research Center
Contacts:
Individual: Thomas L. Bott
Organization:Stroud Water Research Center
Position:Research Scientist Emeritus
Address:
970 Spencer Road,
Avondale, PA 19311 USA
Phone:
tel. 610-268-2153, ext. 1224 (voice)
Email Address:
tlbott@stroudcenter.org
Associated Parties:
Individual:Dr. J. Denis Newbold
Organization:Stroud Water Research Center
Role:Conservative tracer modeling, data analysis
Individual: Floyd Ritter
Organization:Stroud Water Research Center
Role:Field work (P1), sensor maintenance, laboratory analyses, data preparation
Individual: Jean Pierson
Organization:Stroud Water Research Center
Role:Chemical analyses (P1)
Individual: Cindy Dunn
Organization:Stroud Water Research Center
Role:Data analysis (P1)
Individual: David Montgomery
Organization:Stroud Water Research Center
Role:Field work (P2), sensor maintenance, laboratory analyses, data analysis
Individual: Bruce Wallace
Organization:Stroud Water Research Center
Role:Field work (P2), sensor maintenance, laboratory analyses
Individual: Chad Colburn
Organization:Stroud Water Research Center
Role:Field work (P2), sensor maintenance, laboratory analyses
Individual: Nancy Parsons
Organization:Stroud Water Research Center
Role:Field work (P2)
Individual: Brian Hughes
Organization:Stroud Water Research Center
Role:Chlorophyll sample analysis (P2)
Individual: Michael Gentile
Organization:Stroud Water Research Center
Role:Chemical analyses (P2)
Individual: Sherman Roberts
Organization:Stroud Water Research Center
Role:Chemical analyses (P2)
Individual: Melanie Arnold
Organization:Stroud Water Research Center
Role:Data analysis (P2)
Individual: Robert Fox
Organization:Stroud Water Research Center
Role:Data analysis (P2)
Individual: Erica Zwilling
Organization:Stroud Water Research Center
Role:Data analysis (P2)
Individual:Dr. Charles L. Dow
Organization:Stroud Water Research Center
Role:Data analysis (P1 and P2)
Individual: Heather Brooks
Organization:Stroud Water Research Center
Role:Data analysis (P2)
Individual: Timothy Smith
Organization:Stroud Water Research Center
Id:https://orcid.org/0009-0008-2287-8072
Role:Data analysis (P2)
Metadata Providers:
Individual: Timothy S. Smith
Organization:Stroud Water Research Center
Position:Data Analyst
Email Address:
tsmith@stroudcenter.org
Id:https://orcid.org/0009-0008-2287-8072

Temporal, Geographic and Taxonomic Coverage

Temporal, Geographic and/or Taxonomic information that applies to all data in this dataset:

Time Period
Begin:
1971-04-07
End:
2010-01-21
Geographic Region:
Description:Three third-order study reaches located on the east branch of White Clay Creek, Chester co., PA, a tributary of the Christina River in the Delaware River Watershed. Data were collected in two periods. In the first period (P1), there were two study reaches - one in permanent forest (sampled 1971-1974); the other approximately 500 meters downstream, in meadow (1973-1975). Between the first and second periods, the riparian zone of the meadow reach was reforested. In the second period (P2), study reaches were - the one in permanent forest (1997-2010); the former meadow reach, now reforested (2005-2010); and a new meadow reach approximately 600 meters downstream of the bottom of the reforested reach (1997-2010). Reach length was between 150 and 200 meters. The coordinates for the bottom of each reach is as follows: Forested (39.863222° N, -75.78433°W) Reforested (39.85907°N, -75.783641°W) Meadow (39.854803°N, -75.784339°W)
Bounding Coordinates:
Northern:  39.87Southern:  39.85
Western:  -75.795Eastern:  -75.774

Project

Parent Project Information:

Title:Ecosystem metabolism and associated environmental data for a forested, meadow and reforested reach of White Clay Creek, Chester Co., Pennsylvania; 1971-1975 and 1997-2010
Personnel:
Individual:Dr. Thomas L. Bott
Organization:Stroud Water Research Center
Role:Principal Investigator
Abstract:

Ecosystem metabolism data for a 3rd-order Piedmont stream were collected during two periods: P1- April 1971 – Dec 1975, and P2- May 1997 – January 2010. Measures were made in a meadow and a forested reach during each period and in a reforested (formerly meadow) reach during the latter years of P2. During P1, measures were made by transferring streambed substrata to chambers in water jackets located on the streambank and measuring dissolved oxygen changes over diel periods. During P2, open system measures of dissolved O2 change were made for several days in warm and cold seasons, with reaeration determined from a propane injection experiment. Metabolism estimates were determined from diel curves of dissolved O2 change. Photosynthetically active radiation (PAR) and chlorophyll were measured concurrent with many measurements in P1 and all measures during P2, and temperature with all measures. Water chemistry parameters (NH4-N, NO3-N, PO4-P, SiO2, Cl, SO4, total alkalinity, pH) associated with each run are included in the data set, as are days since storm of various thresholds.

Additional Award Information:
Funder:Rockefeller Foundation and Boyer Endowment
Title:Rockefeller Foundation and Boyer Endowment Fund
Additional Award Information:
Funder:National Science Foundation (NSF) and U.S. Environmental Protection Agency (EPA)
Title:DEB: 9613588
Additional Award Information:
Funder:National Science Foundation (NSF)
Title:DEB: 424681
Additional Award Information:
Funder:National Science Foundation (NSF)
Title:DEB: 9726986
Additional Award Information:
Funder:Stroud Water Research Center
Title:Pennswood 2 Endowment
Related Project:
Title:A study of the White Clay Creek watershed, 1969-1974
Personnel:
Individual:Dr. Ruth Patrick
Organization:Academy of Natural Sciences of Philadelphia
Role:Principal Investigator
Individual:Dr. Robin Vannote
Organization:Stroud Water Research Center
Position:Director
Role:Principal Investigator
Additional Award Information:
Funder:Rockefeller Foundation and Boyer Endowment
Title:Rockefeller Foundation and Boyer Endowment Fund
Related Project:
Title:Streamside reforestation: An analysis of ecological benefits and societal perceptions
Personnel:
Individual:Dr. Bernard Sweeney
Organization:Stroud Water Research Center
Position:Director
Role:Principal Investigator
Additional Award Information:
Funder:National Science Foundation (NSF) and U.S. Environmental Protection Agency (EPA)
Title:DEB: 9613588
Related Project:
Title:LTREB: Stream ecosystem structure and function within a maturing deciduous forest
Personnel:
Individual:Dr. Louis Kaplan
Organization:Stroud Water Research Center
Role:Principal Investigator
Additional Award Information:
Funder:National Science Foundation (NSF)
Title:DEB: 424681
Additional Award Information:
Funder:National Science Foundation (NSF)
Title:DEB: 9726986
Related Project:
Title:Ecosystem Metabolism Measure Stroud Water Research Center
Personnel:
Individual:Dr. Thomas Bott
Organization:Stroud Water Research Center
Role:Principal Investigator
Individual:Dr. Bernard Sweeney
Organization:Stroud Water Research Center
Position:Director
Role:Co-Principal Investigator
Additional Award Information:
Funder:Stroud Water Research Center
Title:Pennswood 2 Endowment of the Stroud Water Research Center

Maintenance

Maintenance:
Description:

Ongoing data collection.

Frequency:asNeeded
Other Metadata

Additional Metadata

additionalMetadata
        |___text '\n    '
        |___element 'metadata'
        |     |___text '\n      '
        |     |___element 'unitList'
        |     |     |___text '\n        '
        |     |     |___element 'unit'
        |     |     |     |  \___attribute 'id' = 'Days'
        |     |     |     |  \___attribute 'name' = 'Days'
        |     |     |     |___text '\n          '
        |     |     |     |___element 'description'
        |     |     |     |     |___text 'The values contained are measured in days since an event.'
        |     |     |     |___text '\n        '
        |     |     |___text '\n        '
        |     |     |___element 'unit'
        |     |     |     |  \___attribute 'id' = 'MolQuantaPhotonPerMeterSquaredPerDay'
        |     |     |     |  \___attribute 'name' = 'MolQuantaPhotonPerMeterSquaredPerDay'
        |     |     |     |___text '\n          '
        |     |     |     |___element 'description'
        |     |     |     |     |___text 'Mol quanta of photons of photosynthetically active radiation (PAR) per meter2 per day'
        |     |     |     |___text '\n        '
        |     |     |___text '\n        '
        |     |     |___element 'unit'
        |     |     |     |  \___attribute 'id' = 'MilligramCaCO3PerLiter'
        |     |     |     |  \___attribute 'name' = 'MilligramCaCO3PerLiter'
        |     |     |     |___text '\n          '
        |     |     |     |___element 'description'
        |     |     |     |     |___text 'Milligrams of Calcium Carbonate per Liter of water'
        |     |     |     |___text '\n        '
        |     |     |___text '\n        '
        |     |     |___element 'unit'
        |     |     |     |  \___attribute 'id' = 'Unitless'
        |     |     |     |  \___attribute 'name' = 'Unitless'
        |     |     |     |___text '\n          '
        |     |     |     |___element 'description'
        |     |     |     |     |___text 'Ratio units cancel out'
        |     |     |     |___text '\n        '
        |     |     |___text '\n        '
        |     |     |___element 'unit'
        |     |     |     |  \___attribute 'id' = 'GramsOxygenPerMeterSquaredPerDay'
        |     |     |     |  \___attribute 'name' = 'GramsOxygenPerMeterSquaredPerDay'
        |     |     |     |___text '\n          '
        |     |     |     |___element 'description'
        |     |     |     |     |___text 'Grams of Oxygen per square meter per day'
        |     |     |     |___text '\n        '
        |     |     |___text '\n        '
        |     |     |___element 'unit'
        |     |     |     |  \___attribute 'id' = 'LogUnits'
        |     |     |     |  \___attribute 'name' = 'LogUnits'
        |     |     |     |___text '\n          '
        |     |     |     |___element 'description'
        |     |     |     |___text '\n        '
        |     |     |___text '\n      '
        |     |___text '\n    '
        |___text '\n  '

Additional Metadata

additionalMetadata
        |___text '\n    '
        |___element 'metadata'
        |     |___text '\n      '
        |     |___element 'emlEditor'
        |     |        \___attribute 'app' = 'ezEML'
        |     |        \___attribute 'release' = '2023.05.11'
        |     |___text '\n    '
        |___text '\n  '

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