ON-LINE VERSION
A DATA SET is a series of observations collected by the same methodology. Each data set should have documentation sufficient for someone unfamiliar with the research to replicate the study. Data sets may be broken into subsets (data files) that are discrete in space and time, in that order. The documentation for a data set should include all spatial and temporal subdivisions of the data.
(Data, Abstract, Methods, Variables)
NOTES:
| PERSON(S) COMPLETING THIS FORM: | E-MAIL ADDRESS: |
William H. McDowell |
wmcdowell@lternet.edu |
Eda C. Meléndez-Colom |
emelendez@lternet.edu |
DATA SET IDENTIFIER: Chemistry of rainfall, throughfall, and stream water from El Verde and Bisley Verde and Bisley stations
PROJECT TITLE: Precipitation and Stream Chemistry
PROJECT DESCRIPTION: Soil organic matter content (SOM) and C:N ratios of the litter (Weaver et al. 1973, Zou et al. 1995) and SOM (Silver et al. 1999) increase with elevation and are expected to influence stream chemistry (Aitkenhead & McDowell 2000). Linking stream chemistry to characteristics of watershed soils and vegetation (litter quality, soil C:N, soil C and N standing stocks) can be done within the timeframe of the current funding request.
Rain, throughfall, and stream water are collected weekly at 18 LEF sites. These data cover the period from 1988 onwards. Earlier rain and stream water chemistry data are in the files from William McDowell.
LTER CORE AREAS: Annotate all that apply (See online list)
| Inorganic Inputs and Nutrient Movement |
LEF LTER 1 RESEARCH TOPIC: (Annotate all that apply) (See online list)
| Environmental Monitoring |
We define a data file as a component of a data set. A data set can have
only one data file or more. Basically, different data files have different data
structures or format .
DATA
SET FILES (SUBSETS):
| 0 | All sites basic field data | BasicFieldData.txt | 27-Dec-1988
|
weekly | 28-Jun-2011 |
| 1 | Quebrada Sonadora (QS) | QuebradaSonadora.txt | 3-Jun-1983 | weekly | 26-Dec-2007 |
| 2 | Quebrada Toronja (QT) | QuebradaToronja.txt | 24-May-1983 | weekly | 27-Dec-2005 |
| 3 | Rio Icacos (RI) | RioIcacos.txt | 24-May-1983 | weekly | 26-Dec-2007 |
| 4 | Puente Roto Mameyes (MPR) | RioMameyesPuenteRoto.txt | 16-May-1989 | weekly | 26-Dec-2007 |
| 5 | Quebrada uno-Bisley (Q1) | QuebradaCuenca1-Bisley.txt | 20-May-1986 | weekly | 26-Dec-2007 |
| 6 | Quebrada dos-Bisley (Q2) | QuebradaCuenca2-Bisley.txt | 20-May-1986 | weekly | 26-Dec-2007 |
| 7 | Quebrada tres-Bisley (Q3) | QuebradaCuenca3-Bisley.txt | 20-May-1986 | weekly | 26-Dec-2007 |
| 8 | Quebrada Prieta A (QPA) | QuebradaPrieta-A.txt | 06-Jun-1989 | weekly | 19-Oct-1999 |
| 9 | Quebrada Prieta B (QPB) | QuebradaPrieta-B.txt | 06-Jun-1989 | weekly |
23-Sep-1997 |
| 10 | Rain Collector-Bisley (RCB) | RainCollector-Bisley.txt | 23-Mar-1988 | weekly | 26-Dec-2007 |
| 11 | Rain Collector-El Verde (RCEV ) | RainCollector-ElVerde.txt | 21-Nov-1983 | weekly | 26-Dec-2007 |
| 12 | Throughfall-Bisley (TFB=TCB) | Throufall-Bisley.txt | 10-Jun-1986 | weekly | 26-Dec-2007 |
| 13 | Wet Dry-El Verde (WDEV) | WetDry-ElVerde.txt | 11-Dec-1984 | weekly | 26-Dec-2007 |
| 14 | Bisley Gap (BGAP) | BisleyGap.txt | 01-Aug-1989 | weekly | 21-Jan-1997 |
| 15 | Quebrada Prieta (QP) | QuebradaPrieta.txt | 26-Oct-1999 | )weekly | 26-Dec-2007 |
| 16 | Rio Mameyes Gage (MG) | RioMameyesGage.txt | 29-Sep-1997 | weekly | 26-Dec-2007 |
| 17 | Quebrada Guaba (QG) | QuebradaGuaba.txt | 25-Jan-2000 | weekly | 26-Dec-2007 |
RESEARCH LOCATION: Streams and rain collectors described and listed in the site's description and data files.
| William H. McDowell | wmcdowell@lternet.edu |
| Frederick Scatena | fscatena@lternet.edu |
Douglas Schaefer |
| William H. McDowell | (603) 862-2249 | wmcdowell@lternet.edu |
SOURCE OF FUNDING (SPONSOR): NSF-LTER
DATA
SET ABSTRACT: Rain, throughfall, and stream water are
collected weekly at the LEF sites listed below. These data sets begin as early
as 1983; LTER sampling began in 1988.
Rain and throughfall samples are the
total catch for the week, and are exposed to field conditions for that time.
No event sampling is conducted on a routine basis. Stream water samples are
grab samples taken from the water/air interface at stream channel center on
the sampling day (usually Tuesdays). Rain samples from WDEV are wet only from
an automatically-closing collector that prevents any dry deposition (Aerochem
Metrics NADP collector). RCEV and RCB are bulk or always-open collectors that
receive dry deposition by sedimentation.
A continuous record of stream stage (height)
is recorded by a datalogger at all ongoing stream sampling sites. Average daily
streamflows are available from the USGS and at other locations (Hydrology and
Meteorology) on this site.
All samples are measured for pH and conductivity,
and then filtered (pre-combusted Whatman GF/F glass fiber filter) prior to further
analysis. From 1983-1994 samples were cooled and returned to the San Juan chemistry
laboratory for analysis. During those years, samples for NH4 and
NO3 analyses were refrigerated continuously until analysis. Subsamples
for NH4 analysis were also preserved with 1 molar HCl. From 1994
on, samples for NH4 and NO3 were frozen until analysis,
were not acidified, and all analyses were conducted at the University of New
Hampshire.
Rain, Throughfall, and Stream water
Sampling Sites
Descriptions of LTER LUQ rain, throughfall, and stream water weekly sample chemistry
data from 1988 onwards. Chemical concentrations are recorded as mg/L or mg/L
as appropriate. Values below detection limits are recorded as 1/2 the detection
limit.
Site |
Abbreviation |
Description |
Comments |
Rain collector Bisley . |
RCB |
Bulk collector. |
|
Rain collector El Verde |
RCEV |
Bulk collector. |
|
Wet/dry El Verde . |
WDEV. |
Wet only collector. |
|
Throughfall Bisley. |
TFB=TCB |
TF bulk 10-collector composite. |
|
Bisley gap . |
BGAP . |
TF bulk 10-collector composite. |
|
Quebrada Sonadora . |
QS |
El Verde stream. |
|
Quebrada Toronja . |
QT . |
El Verde stream. |
|
Quebrada Toronja 1 |
QT1 |
El Verde stream |
|
Quebrada Prieta A. |
QPA |
El Verde stream. |
|
Quebrada Prieta B . |
QPB |
El Verde stream. |
|
Quebrada Prieta |
QP |
El Verde stream |
|
Rio Mameyes Puente Roto. |
MPR(1). |
Bisley stream . |
(1)Previously "PRM" |
Quebrada Cuenca 1 |
Q1 . |
Bisley stream. |
|
Quebrada Cuenca 2 |
Q2 |
Bisley stream . |
|
Quebrada Cuenca 3 |
Q3 . |
Bisley stream. |
|
Rio Mameyes Gage |
MG |
Bisley stream |
|
Rio Icacos |
RI |
LEF South stream |
|
Quebrada Guaba |
QG |
Bisley stream | Near Naguabo |
DATA
SET METHODS:
Analytical
Techniques
pH - Electrometric with combination electrode
Conductivity - Conductivity bridge
Cl - up to 1989 by automated colorimetric analysis (thiocyanate); after 1989
by liquid chromatography with conductivity detection
NO3-N - up to 1989 by automated colorimetric analysis (Cd-Cu reduction); after
1989 by liquid chromatography with UV or conductivity detection
SO4-S - Liquid chromatography, conductivity detection
Na, K, Mg, and Ca - up to 1994 by atomic absorption spectroscopy; after 1994
by ion chromatography with conductivity detection
NH4-N - automated colorimetric analysis (phenolhypochlorite)
PO4-P - automated colorimetric analysis (molybdate blue)
DOC - up to 1998 by persulfate oxidation (McDowell et al. 1997); after 1998
by high temperature catalytic oxidation
DIC - by syringe stripping and infrared spectroscopy (Stainton 1973).
TDN - prior to 1998 by persulfate oxidation and automated colorimetric analysis;
after 1998 by high temperature catalytic oxidation with chemiluminescent detection
TDP - by persulfate digestion followed by automated colorimetric analysis
SiO2 - automated colorimetric analysis (molybdate blue)
DON - by difference (TDN - NO3-N - NH4-N)
Table 1. Data Abbreviations, Detection Limits, and Units of Measure
Datum |
Abbreviation |
Detection limit |
Units |
Discharge |
Discharge |
|
Cubic feet per second |
Gage height |
Gage_Ht |
|
feet |
pH |
pH |
|
pH units |
Conductivity |
Cond |
|
micromho/cm |
Chloride |
Cl |
0.1 |
mg/L |
Nitrate |
NO3-N |
3-10 |
ug N/L |
Sulfate |
SO4-S |
0.1 |
mg/L as S |
Sodium |
Na |
0.1 |
mg/L |
Potassium |
K |
0.05 |
mg/L |
Magnesium |
Mg |
0.1 |
mg/L |
Calcium |
Ca |
0.1 |
mg/L |
Ammonium |
NH4-N |
2-10 |
ug N/L |
Soluble Reactive Phosphate |
PO4-P |
3 |
ug N/L |
Dissolved Organic Carbon |
DOC |
0.1 |
mg/L |
Dissolved Inorganic Carbon |
DIC |
|
mg/L |
Total Dissolved Nitrogen |
TDN |
0.1 |
mg/L |
Total Dissolved Phosphorus |
TDP |
3 |
mg/L |
Silica |
SiO2 |
0.1 |
mg/L as SiO2 |
Dissolved Organic Nitrogen |
DON |
0.1 |
mg/L |
REFERENCES:
McDowell,
W.H., J.J. Cole, and C.T. Driscoll. 1987. Simplified version of the ampoule-persulfate
method for determination of dissolved organic carbon. Can. J. Fish. Aquat. Sci.
44:214-218.
Stainton, M.P. 1973. A syringe gas-stripping procedure for gas chromatographic
determination of dissolved inorganic and organic carbon in fresh water and carbonates
in sediments. J. Fish. Res. Bd. Can. 30:1441-1445.
CROSS-REFERENCES
(other data sets related to this one):
SAMPLE LOCATION: ITES, Chemistry Laboratory
STORAGE SITES(of data files): ITES, Data Manager's File DM-001 , Drawer #2
INVESTIGATOR'S ASSIGNED KEYWORDS: Biogeochemical cycles, nutrient input/output relationships, ammonium, nitrate, sulfate, chloride, potassium, sodium, calcium, magnesium
LEF LTER OFFICIAL KEYWORDS (See table): BISLEY GAPS, EL VERDE, Q MAMEYES, Q PRIETA, Q TORONJA, Q ICACOS, RAIN, RIVER, BIOGEOCHEMICAL CYCLES, CATIONS AND ANIONS, NITROGEN, DISCHARGE, PEER REVIEWED JOURNAL
PUBLICATIONS:
McDowell, W.H., C. Gines-Sanchez, C.E.
Asbury, and C.R. Ramos-Perez. 1990. Influence of sea salt aerosols and long-range
transport on precipitation chemistry at El Verde, Puerto Rico. Atmospheric Environment
24A:2813-2821.
McDowell, W.H. and C.E. Asbury. 1994. Export of carbon, nitrogen, and major ions from three tropical montane watersheds. Limnology and Oceanography 39:111-125.
Schaefer, D.A., W.H. McDowell, F.N. Scatena, and C.E. Asbury. 2000. Effects of hurricane disturbance on stream water concentrations and fluxes in eight watersheds of the Luquillo Experimental Forest, Puerto Rico. J. Tropical Ecology 16:189-207.
RESTRICTED ___ UNRESTRICTED _X__
REASONS TO RESTRICT DATA IN THIS DATA SET BEYOND ITS TWO YEAR POLICY PERIOD*:
*WILL HAVE TO BE APPROVED BY AT LEAST ONE LUQ LTER PRINCIPAL INVESTIGATORS: N. Brokaw, J. ZIMMERMAN, A. LUGO
_X_ "File" copy only:Data Management will only file an electronic
copy of the data file and its documentation
___ " Enter" data on-line:Data Management will be in charge
of entering the data on computer files (Contact Eda
C. Meléndez)
SITES
DESCRIPTIONS:
The study site was the Luquillo Experimental
Forest on the eastern end of Puerto Rico (18 15'N, 65 50'W). The Luquillo Experimental
Forest is synonymous with the Caribbean National Forest and has been administered
by the U.S. Forest Service for ~70 yrs. Elevation ranges from 200 to 1,000m.
The plan community is dominated by tabonuco (Dacryodes excelsa) forest
type at elevations of 200-600m adn the colorado (Cyrilla racemiflora)
forest type at elevations of 600-750 m. On ridges and peaks above 750 m, vegetation
consists of short-statured elfin forest. Palms (most commonly Prestoea montana)
are found throughout the forest but are especially common along streams channels
and in poorly drained areas. Human disturbance, consisting of small farms and
selective tree harvesting (mostly at lower elevations), preceded Forest Service
administration. Scattered plantation forests have been established since designation
of the area as an experimental forest (Brown et al. 1983).
Precipitation ranges from 250 to >500 cm yr-1 in the Luquillo
Forest area and increases with elevation. Precipitation peaks in May and from
August to November (McDowell and Estrada-Pinto 1988). Hurricanes and tropical
depressions produce individual rainfall events that are highly unpredictable
and very intense, and hurricanes are thought to play a major role in structuring
plant community dynamics (Brown et al. 1983).
The following table summarizes the features of the studied watersheds:
Table 2. Characteristics of three of the long-term study watersheds
Icacos |
Sonadora |
Toronja |
|||||
Elevation (m) |
616-800 |
375-1,050 |
267-510 |
||||
Aspect |
S |
NW |
NW |
||||
Area (ha) |
326 |
362 |
16.2 |
||||
Bedrock |
Quartz diorite |
Andesite, mudstone |
Andesite, mudstone |
||||
Soil |
Utuado clay |
Los Guineos clay |
Los Guineos clay |
||||
Vegetation types |
|||||||
Tabonuco (%) |
0 |
6 |
100 |
||||
| Colorado (%) | 75 |
57 |
0 |
||||
| Palm (%) | 24 |
25 |
0 |
||||
1 |
12 |
0 |
|||||
| Channel slope (%) | 1.4 |
24 |
20 |
||||
Channel substrate |
Sand, boulders |
Boulders, cobbles |
Clay cobbles |
||||
Geographical positional system (GPS) Coordinates for each location:
location | latitude | longitude |
File Name or # above (all in which the variable appears) |
all | all | all | all | all (except 0, 10, 11, 12, 13, 14) |
AbbreviationAbbreviation(as it appears on the data file) |
Code |
Sample_ID | Sample_Date | Sample_Time | USGS_Stream_Flow_CFPS |
| Sample Code | Watershed or Collector's location |
Sampling date | Sampling time | Streamflow | |
Numeric code of sample assigned at ITES |
Watershed or Collector's location where the sample is taken |
Date of sampling (in mm/dd/yyyy). Pre-LUQ LTER period:03-Jun-83 to 17-Mar-87 (with gaps); LUQ LTER Period:25-Oct-88 to present |
Time of sampling in integer format | Discharge as measured by a USGS streamflow station to the nearest 15 minutes to sampling time | |
|
cubicFeetPerSecond | ||||
±0.1 |
|||||
| 1028,... | {MG, MPR, Q1, Q2, Q3, QP, QPA, QPB, QS, QT, QT1, RCB, RCEV, TCB, WDEV, RI, QG} |
|
|||
| integer | alphanumeric | datetime | datetime | decmal | |
| blank | none | blank | blank | blank |
VARIABLES (ATTRIBUTES):
File Name or # above (all in which the variable appears) |
0 | 0 | 0 | 0 | 0 |
AbbreviationAbbreviation(as it appears on the data file) |
Gage_Ht | Temp | pH |
Cond |
REMARKS |
| Gage height | Temperature | pH |
Conductivity |
REMARKS | |
| Gage Height at sampling time (in meter - see note) | Temperature of sample at sampling time | pH (Electrometric with combination electrode) | Conductivity (Conductivity bridge in micromho/cm ) | Comments about the conditions found ast the field in the time of collection and/or the data entered | |
| meter | celsius |
|
|
||
±0.1 |
±0.01 | ±.01 |
±.01 |
||
| decmal | decmal | decimal |
decimal |
alphanumeric | |
| blank | blank | blank |
blank |
Note: This unit was display as "feet" until April 10, 2008. This should be corrected as "meter";this was a typo not a change of measuring method.
VARIABLES (ATTRIBUTES):
File Name or # above (all in which the variable appears) |
All (except 0) |
All (except 0)l |
All (except 0) |
All (except 0) |
All (except 0) |
AbbreviationAbbreviation(as it appears on the data file) |
Chloride |
Nitrate |
Sulfate-S |
Sodium |
Potassium |
Chloride |
Nitrate Nitrogen |
Sulfate |
Sodium |
Potassium |
|
| Chloride (up to 1989 by automated colorimetric analysis (thiocyanate); after 1989 by liquid chromatography with conductivity detection) in ug Cl/L | Nitrate Nitrogen (up to 1989 by automated colorimetric analysis (Cd-Cu reduction); after 1989 by liquid chromatography with UV or conductivity detection) in ug N/L | Sulfate (Liquid chromatography, conductivity detection) in mg/L | Sodium (up to 1994 by atomic absorption spectroscopy; after 1994 by ion chromatography with conductivity detection) in mg/L | Potassium (up to 1994 by atomic absorption spectroscopy; after 1994 by ion chromatography with conductivity detection) in ug N/L | |
microgramsPerLite |
microgramsPerLiter |
milligramsPerLiter |
milligramsPerLiter |
milligramsPerLiter |
|
±.01 |
±.01 |
±.01 |
±.01 |
±.01 |
|
decimal |
decimal |
decimal |
decimal |
decimal |
|
blank |
blank |
blank |
blank |
blank |
VARIABLES (ATTRIBUTES):
File Name or # above (all in which the variable appears) |
All (except 0) |
All (except 0) |
All (except 0) |
All (except 0) | All (except 0) |
AbbreviationAbbreviation(as it appears on the data file) |
Magnesium |
Calcium |
NH4 |
PO4 | NPOC |
Magnesium |
Calcium |
Ammonium Nitrogen |
Phosphate | Dissolved Organic Carbon | |
| Magnesium (up to 1994 by atomic absorption spectroscopy; after 1994 by ion chromatography with conductivity detection) in mg/L | Calcium (up to 1994 by atomic absorption spectroscopy; after 1994 by ion chromatography with conductivity detection) in mg/L | Ammonium Nitrogen[automated colorimetric analysis (phenolhypochlorite)] in ug N/L | Phosphate [automated colorimetric analysis (molybdate blue)] in ug P/L | Dissolved Organic Carbon (up to 1998 by persulfate oxidation (McDowell et al. 1997); after 1998 by high temperature catalytic oxidation) in mg C/L | |
milligramsPerLiter |
milligramsPerLiter |
microgramsPerLiter |
microgramsPerLiter | milligramsPerLiter | |
±.01 |
|||||
decimal |
decimal |
decimal |
decimal |
decimal |
|
blank |
blank |
blank |
blank |
blank |
VARIABLES (ATTRIBUTES):
File Name or # above (all in which the variable appears) |
All (except 0) |
All (except 0) |
All (except 0) | All (except 0) | All (except 0) | All (except 0) |
AbbreviationAbbreviation(as it appears on the data file) |
DIC | TDN | TDP | SiO2 | DON | TSS |
| Dissolved Inorganic Carbon | Total Dissolved Nitrogen | thiamin diphosphate | Silica | Dissolved Organic Nitrogen |
Total Suspended Sediments |
|
| Dissolved Inorganic Carbon [by syringe stripping and infrared spectroscopy (Stainton 1973).] in mg C/L | Total Digestible Nutrients (prior to 1998 by persulfate oxidation and automated colorimetric analysis; after 1998 by high temperature catalytic oxidation with chemiluminescent detection) in mg N/L | thiamin diphosphate (by persulfate digestion followed by automated colorimetric analysis) in ug P/L | Silica [automated colorimetric analysis (molybdate blue)] in mg SiO2/L | Dissolved Organic Nitrogen [by difference (TDN - NO3-N - NH4-N)] in mg N/L |
Total Suspended Sediments in mg/L | |
| milligramsPerLiter | milligramsPerLiter | microgramsPerLiter | milligramsPerLiter |
milligramsPerLiter |
milligramsPerLiter |
|
|
|
|||||
decimal |
decimal |
decimal |
decimal |
decimal |
decimal |
|
blank |
blank |
blank |
blank |
blank |
blank |
COMPUTATIONAL METHODS:
FOR DATA MANAGER USE ONLY
DATE OF LAST REVIEW: