do ‘payments for ecosystem services’ promote soil carbon ... · c sink methods total c measured...
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C Sink MethodsTotal C measured at the soil analysis lab at Univ.
of Costa RicaActive C via permanganate-oxidizable C (POxC) in the lab
Do PES programs sequester C belowground?
Cumulative Soil Respiration unaffected by PES Land UseSpecific CO2 is lowest in Conservation Forests
C Source Results
Do ‘Payments for Ecosystem Services’ promote soil carbon sequestration in the tropics?Andreas G. Khechfe*1,2, A. Peyton Smith3, Katherine Quiñonez-González3, Malak M. Tfaily4, Jane Fudyma4, Kelly Brumbelow5, Georgianne W. Moore2
*1Undergraduate, Humboldt State University, Dept. of Environmental Science and Management; 2Texas A&M University (TAMU), Ecosystem Science and Management; 3TAMU, Soil and Crop Sciences, 4 University of Arizona, Dept. of Soil, Water and Environmental Science,5TAMU, Civil and Environmental Engineering
Forest Species & Site, not PES, affects Total and Active Soil Carbon
Site, rather than PES, altersmolecular composition of SOM
RationalePayments for ecosystem services (PES) programs support afforestation & forest conservation activities intended to enhance carbon (C) sequestration in tree biomass. Yet, soils hold two-to-three times as much C than trees. With increasing interest in managing land for C sequestration, we ask
Take Home MessageSoils at PES sites appear more efficient at using soil C for respiration than agricultural sites suggesting that there may be more stabilized C at PES sites. Identifying the amount and nature (i.e., stability) of soil C stored may reveal an unidentified sink of C for PES ecosystems.
HypothesesWe hypothesize that the increase in the abundance and diversity of C inputs from forest cover in PES ecosystems will result in greater potential for soil C sequestration.
Experimental ApproachTo determine the C source and sink potential of soils from PES plantations & forests, we measured C source (CO2 burst test) and sink (total organic carbon, active carbon and the molecular composition of soluble C) in PES site & in adjacent agricultural sites (i.e., represents
prior land use) across sites in North-Central Costa Rica.
Funding for this Research Experiences for Undergraduate program is provided by the National Science Foundation’s Division of Earth Sciences (EAR-1659848). Special thanks to Mr. Carlos Porras and FUNDECOR (Fundación para el Desarrollo de la Cordillera Central Volcánica) for their collaboration in this study in the logistics for selecting the PES sites; Don Eugenio Gonzalez- Jimenez and the personnel of the Soltis Center. Thanks also to Kaiya Weatherby, Glen Aguilar, and Melissa Zapata, fellow REU students, for helping with this study.
Costa Rica
PES Sites1. Ecosistemas2. Rio Peje3. Gamboa4. Soltis
Lipids
Lignin Tannins
Condensed Hydrocarbons
Unsa
t. HC
Proteins Amino Sugars
Carbo-hydrates
Hydr
ogen
-to-C
arbo
n Ra
tio
Oxygen-to-Carbon Ratio
-MS
300 400 500 600 700 800 900 m/z0
1
2
3
4
5
7x10Intens.
m/z
Negative-Ion electrospray Ionization FT-ICR MS at 12 TeslaSuwannee River Fulvic Acid (SRFA)10,000 peaks > S/N=7 (200 < m/z < 1000)m/Δm50% > 1000,000 at m/z 500
Ecosistemas Gamboa Hacienda Rio Peje Soltis Center
0
20
40
60
80
100
0
400
800
1200
1600
2000
D. marginata Pasture Grasses H. alchorneoides T. amazonia V. guatemalensis Mixed Species
Agriculture Forest Plantation Conservation Forest
Ecosistemas Gamboa Hacienda Rio Peje Soltis Center
C-C
O2
(!g
g-1so
il)C-
CO2
(!g
g-1so
il C)
Agriculture Plantation Cons. Forest
Ecosistemas Gamboa Rio Peje Soltis
a
b
C Source MethodsCumulative C-CO2 measured via 24 h incubation under constant temperature & moisture. (i.e. CO2burst test)
Direct headspace injection into PP Systems EGM-5
Soils (0-5 cm) were collected in 3 land uses across 4 sites, N = 3 samples per site. Soils were oven dried at 50ºC before analyses
The molecular composition of C via high resolution mass spectrometry, Fourier transform ion cyclotron resonance (FT-ICR MS) from soil-water extracts.
Tota
l C_m
g/kg
POxC
_mg/
kg
0.0e+0
5.0e+4
1.0e+5
1.5e+5
2.0e+5
0
300
600
900
1200
D. marginata Pasture grasses
H. alchorneoides
T. amazona V. guatemalensis
Mixed Species
Agriculture Plantation Cons. Forest
Total C_mg/kgEcosistemasGamboaRioPejeSoltisEcosistemasGamboaRioPejeSoltis
POxC_mg/kg
Ecosistemas
GamboaRioPejeSoltis
POxC_mg/kgEcosistemasGamboaRioPejeSoltis
Soil
Carb
on (m
g kg
-1)
Activ
e C
(mg
kg-1
)
Agriculture Plantation Cons. Forest
a
bab ab
ab
ab
a
b
ab ab
abab
Ecosistemas Gamboa Rio Peje Soltis Agriculture Plantation Native Forest
H/C
0.5
1.0
1.5
2.0
2.5
0.0 0.2 0.4 0.6 0.8 1.0 1.2 0.0 0.2 0.4 0.6 0.8 1.0 1.2 0.0 0.2 0.4 0.6 0.8 1.0 1.2O/C
ClassAminoSugarCarbConHCLigninLipidNoneOtherProteinTanninUnsatHC
Agriculture Plantation Native Forest
N R
ows
4.8%8.3%
9.1%
42.7%
6.5%
5.3%
9.3%
2.4%
11.5% 4.3%7.1%
9.4%
44.7%
6.2%
4.5%
8.3%
2.3%
13.2%4.6%
8.3%
9.2%
39.7%
4.7%
4.3%
10.5%
2.3%
16.3%
ClassAminoSugarCarbConHCLigninLipidOtherProteinTanninUnsatHC
Agriculture Plantation Cons. Forest
Agriculture Plantation Cons. Forest
• C composition did not differ between PES and non-PES sites.
Site + Species(Land Use) (p < 0.05)
• PCA shows PES effect differs by site
Ecosistemas Gamboa RioPeje
Prin
2
-5-4-3-2-101234
-6 -5 -4 -3 -2 -1 0 1 2 3 -6 -5 -4 -3 -2 -1 0 1 2 3 -6 -5 -4 -3 -2 -1 0 1 2 3Prin1
Land UseAgricultureNative ForestPlantationAgriculture: (90%)Native Forest: (90%)Plantation: (90%)
Ecosistemas Gamboa Rio Peje
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CO2
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ActiveCarbon
Labile Carbon
SOMTotal Carbon C Sink Results
• There was no effect of PES on cumulative CO2
• Site influenced CO2Gamboa > Rio Peje, Ecosistemas
ab ab
ab
ab
• Carbon use efficiency potentially greater in Cons. Forest.
Van Krevelen diagram used to id compounds
Lignin-like compounds are most abundant
Principal Components Analysis (PCA) of % abundance FT-ICR compounds