Revision date: December 14, 2009
This data set reports the results of a rainfall exclusion experiment in the Tapajos National Forest (Flona-Tapajos) at km 67 along the Santarem-Cuiaba BR-163 highway. From December 1999 through April 2005, following a one-year pre-treatment phase, rainfall was excluded from one of two 1-hectare plots of seasonally dry humid tropical forest. Soil emissions of carbon dioxide (CO2), nitric oxide (NO), nitrous oxide (N2O), and methane (CH4) were monitored in order to determine the likely effect of increasingly frequent El Nino drought episodes in the Amazon basin. Soil trace gas flux data are provided in one comma-separated data file.
Throughfall exclusion panels, Tapajos National Forest. The throughfall exclusion panels drain into wooden gutters constructed in the forest understory. Photos from Nepstad et al., 2002.
Cite this data set as follows:
Davidson, E.A., C.J.R. de Carvalho, R.O. Figueiredo. 2009. LBA-ECO ND-02 Soil Gas Flux, Rainfall Exclusion, km 67, Tapajos National Forest. Data set. Available on-line [http://daac.ornl.gov] from Oak Ridge National Laboratory Distributed Active Archive Center, Oak Ridge, Tennessee, U.S.A. doi: 10.3334/ORNLDAAC/955
The LBA Data and Publication Policy [http://daac.ornl.gov/LBA/lba_data_policy.html] is in effect for a period of five (5) years from the date of archiving and should be followed by data users who have obtained LBA data sets from the ORNL DAAC. Users who download LBA data in the five years after data have been archived must contact the investigators who collected the data, per provisions 6 and 7 in the Policy.
This data set was archived in December of 2009. Users who download the data between December 2009 and November 2014 must comply with the LBA Data and Publication Policy.
Data users should use the Investigator contact information in this document to communicate with the data provider. Alternatively, the LBA Web Site [http://lba.inpa.gov.br/lba/] in Brazil will have current contact information.
Data users should use the Data Set Citation and other applicable references provided in this document to acknowledge use of the data.
Project: LBA-ECO
Activity: Rainfall Exclusion Experiment
LBA Science Component: Nutrient Dynamics
Team ID: ND-02 (Davidson / Carvalho / Dias-Filho / Moller / Moutinho / Sa / Vieira)
The investigators were Belk, Elizabeth Leslie; Carvalho, Claudio Jose Reis de; Davidson, Eric A.; Dias-Filho, Moacyr Bernardino; Figueiredo, Ricardo de Oliveira; Ishida, Francoise Yoko; Markewitz, Daniel and Moutinho, Paulo Roberto de Souza . You may contact Davidson, Eric A. (edavidson@whrc.org) and Figueiredo, Ricardo de Oliveira (ricardo@cpatu.embrapa.br)
LBA Data Set Inventory ID: ND02_REE_Trace_Gas_Tapajos
Changes in precipitation in the Amazon Basin resulting from regional deforestation, global warming, and El Nino
events may affect emissions of carbon dioxide (CO2), methane (CH4), nitrous oxide (N2O), and nitric oxide (NO)
from soils. Changes in soil emissions of radiatively important gases could have feedback implications for
regional and global climate. Here we report the final results of a five-year large-scale (1 ha) throughfall
exclusion experiment, followed by one year of recovery with natural throughfall, conducted in a mature evergreen
forest near Santarem, Brazil. The exclusion manipulation lowered annual N2O emissions in 4 out of 5 treatment
years (a natural drought year being the exception), and then recovered during the first year after the drought
treatment stopped. Similarly, consumption of atmospheric CH4 increased under drought treatment, except during a
natural drought year, and it also recovered to pre-treatment values during the first year that natural
throughfall was permitted back on the plot. No treatment effect was detected for NO emissions during the first
three treatment years, but NO emissions increased in the fourth year under the extremely dry conditions of the
exclusion plot during a natural drought. Surprisingly, there was no treatment effect on soil CO2 efflux in any
year. The drought treatment provoked significant tree mortality and reduced allocation of C to stems, but
allocations of C to foliage and roots were less affected. Taken together, these results suggest that the
dominant effect of throughfall exclusion on soil processes during this six-year period was on soil aeration
conditions that transiently affected CH4, N2O, and NO production and consumption rather than substrate supply.
The Exclusion treatment involves diverting rainfall (throughfall) from a 1-hectare plot using plastic
panels installed in the understory. The Control treatment refers to a similar 1-hectare plot that receives
natural rainfall. A total of 18 gas flux chambers for measurements of CO2, NO, N2O, CH4 were
installed per treatment.
These data were collected by a collaboration of researchers from The Woods Hole Research Center (WHRC), the
Instituto de Pesquisa Ambiental da Amazonia (IPAM), EMBRAPA-CPATU (Belem) and the University of Georgia.
Related Data Sets:
The file Soil_Trace_Gas_Emissions_Tapajos.csv is a comma-delimited file containing the means and standard errors
of the 18 total trace gas emissions measurements per treatment (rainfall exclusion or control) per sampling date
for the Flona Tapajos Rainfall Exclusion Site. For convenience, the Day of year is also provided. The actual
number of repetitions that were included in each mean/standard error is listed in the respective *_reps columns.
Treatment status indicates whether the measurement was made before or after the rain exclusion went into effect.
A -9999 has been listed wherever values are missing. Note that positive values indicate emissions from the soil
to the atmosphere; negative values indicate net uptake by the soils of atmospheric gases.
Data File Description: Soil_Trace_Gas_Emissions_Tapajos.csv
Column Number | Heading | Description |
1 |
Site |
Study Site: Flona-rainfall exclusion |
2 |
Date |
Sample date (YYYY/MM/DD) |
3 |
Day_of_year |
Day of year |
4 |
Treatment_status |
Treatment: pre-exclusion, post-exclusion |
5 |
Treatment |
Treatment class: exclusion, control |
6 |
CO2_mean |
Carbon dioxide, mean |
7 |
CO2_std_err |
Carbon dioxide, standard error |
8 |
CO2_reps |
Carbon dioxide, number of repetitions |
9 |
CO2_units |
Carbon dioxide, measurement units |
10 |
NO_mean |
Nitric oxide, mean |
11 |
NO_std_err |
Nitric oxide, standard error |
12 |
NO_reps |
Nitric oxide, number of repetitions |
13 |
NO_units |
Nitric oxide, measurement units |
14 |
N2O_mean |
Nitrous oxide, mean |
15 |
N2O_std_err |
Nitrous oxide, standard error |
16 |
N2O_reps |
Nitrous oxide, number of repetitions |
17 |
N2O_units |
Nitrous oxide, measurement units |
18 |
CH4_mean |
Methane, mean |
19 |
CH4_std_err |
Methane, standard error |
20 |
CH4_reps |
Methane, number of repetitions |
21 |
CH4_units |
Methane, measurement units |
Example data record:
Site,Date,Day_of_year,Treatment_status,Treatment,CO2_mean,CO2_std_err,CO2_reps,CO2_units, NO_ mean,No_std_err,NO_reps,NO_units,N2O_mean,N2O_std_err,N2O_reps,N2O_units, CH4_mean,CH4_std_err,CH4_reps,CH4_units Flona-rainfall exclusion,1998/09/10,253,pre-exclusion,exclusion,0.14,0.01,18,g C/m2/h, 6.19,1.11,18,ng N/cm2/h,0.62,0.08,16,ng N/cm2/h, -0.90,0.44,16,mg CH4/m2/d Flona-rainfall exclusion,1998/09/10,253,pre-exclusion,control,0.12,0.01,18,g C/m2/h, 3.93,0.47,18,ng N/cm2/h,0.61,0.10,17,ng N/cm2/h, -0.36,0.61,17,mg CH4/m2/d ... Flona-rainfall exclusion,2005/04/12,105,post-exclusion,exclusion,0.10,0.02,18,g C/m2/h, 0.27,0.02,18,ng N/cm2/h,4.52,0.78,18,ng N/cm2/h, -0.37,0.23,18,mg CH4/m2/d Flona-rainfall exclusion,2005/04/12,105,post-exclusion,control,0.09,0.01,18,g C/m2/h, 0.36,0.04,18,ng N/cm2/h,5.54,1.33,18,ng N/cm2/h, -0.26,0.17,18,mg CH4/m2/d |
Site boundaries: (All latitude and longitude given in degrees and fractions)
Site (Region) | Westernmost Longitude | Easternmost Longitude | Northernmost Latitude | Southernmost Latitude | Geodetic Datum |
---|---|---|---|---|---|
Para Western (Santarem) - Rainfall Exclusion Site (Para Western(Santarem)) | - 54.959 | -54.959 | --2.857 | - 2.857 | World Geodetic System, 1984 (WGS-84) |
Changes in precipitation in the Amazon Basin resulting from regional deforestation, global warming, and El Nino events may affect emissions of carbon dioxide (CO2), methane (CH4), nitrous oxide (N2O), and nitric oxide (NO) from soils. Changes in soil emissions of radiatively important gases could have feedback implications for regional and global climate. Here we report the final results of five year of a large-scale (1 ha) throughfall exclusion experiment, followed by one year of recovery with natural throughfall, conducted in a mature evergreen forest near Santarem, Brazil. The exclusion manipulation lowered annual N2O emissions in 4 out of 5 treatment years (a natural drought year being the exception), and then recovered during the first year after the drought treatment stopped. See Davidson et al. (2008) for more information.
The quality of each flux measurement was vetted by the PI. Measurements were discarded if measured concentrations were outside of a reasonable range, or where the tracing of chamber concentrations was too erratic to reliably fit a slope. See Davidson et al. (2008) for more information.
Two 1 ha plots were identified from an initial survey of 20 ha of forest. A 1.5 m deep trench was excavated around the perimeter of the treatment plot to reduce the potential for lateral movement of soil water from the surrounding forest into the plot. A similar trench was excavated around the control plot to avoid the confounding of treatment and trenching effects. All measurements reported here were taken at least 20 m from the trench edge to guard against edge effects.
Plastic PAR-transmitting greenhouse panels were installed in the understory of the exclusion plot only for the
duration of the rainy season. The panels were
installed such that small gaps were left around tree
stems to allow in nutrient-rich stemflow. In all, about half of the annual rainfall was diverted from the
exclusion plot. While they were in place, panels were flipped on their sides every two days to return any
accumulated litter to the forest floor beneath.
Eighteen soil gas flux chambers were installed in each plot for a total of 18 CO2, NO, N2O, CH4 measurements per treatment.
Fluxes of nitric oxide (NO) and carbon dioxide (CO2) were measured in the field using dynamic chambers connected to a Scintrex LMA-3 chemiluminescent analyzer and a LiCor 6252 IRGA. Fluxes of N2O and CH4 were measured by filling syringes with gas from static chamber headspace at 10-minute intervals, and analyzing the samples in a laboratory using gas chromatography.
Discussion of methods can be found in Davidson et al., 2008 and Verchot et al., 1999 and 2000.
This data is available through the Oak Ridge National Laboratory (ORNL) Distributed Active Archive Center (DAAC).
E-mail: uso@daac.ornl.gov
Telephone: +1 (865) 241-3952
Davidson, E.A., D.C. Nepstad, F.Y. Ishida, P.M. Brando. 2008. Effects of an experimental drought and recovery on soil emissions of carbon dioxide, methane, nitrous oxide, and nitric oxide in a moist tropical forest. Global Change Biology 14:2582-2590. DOI: 10.1007/s10533-008-9231-6
Verchot LV, Davidson EA, Cattanio JH, Ackerman IL (2000) Land use change and biogeochemical controls of methane fluxes in soils in eastern Amazonia. Ecosystems 3:41-56. doi:10.1007/s100210000009
Verchot LV, Davidson EA, Cattanio JH, Ackerman IL, Erickson HE, Keller M (1999) Land use change and
biogeochemical controls of nitrogen oxide emissions from soils in eastern Amazonia. Global Biogeochemical Cycles
13:31-34. doi:10.1029/1998GB900019
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