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Land-use change and deep-soil carbon distribution on the Brazilian Amazon-Cerrado agricultural frontier
被引:0
|作者:
V. Popin, Gustavo
[1
]
de Resende, Maria Eduarda B.
[3
]
Locatelli, Jorge L.
[1
]
Santos, Rafael S.
[4
]
Siqueira-Neto, Marcos
[5
]
Brando, Paulo M.
[6
,7
]
Neill, Christopher
[8
]
Cerri, Carlos E. P.
[1
,2
]
机构:
[1] Univ Sao Paulo, Luiz Queiroz Coll Agr, Dept Soil Sci, Ave Padua Dias 11, BR-13418260 Piracicaba, SP, Brazil
[2] Univ Sao Paulo, Ctr Carbon Res Trop Agr CCARBON, Ave Padua Dias 11, BR-13418900 Piracicaba, SP, Brazil
[3] Univ Sao Paulo, Ctr Energia Nucl Agr, Ave Centenario 303, Piracicaba, SP, Brazil
[4] Colorado State Coll, Nat Resource Ecol Lab, Ft Collins, CO 80523 USA
[5] Biofil Ambipar Environm, Ave Angel 2330, BR-01228200 Sao Paulo, SP, Brazil
[6] Yale Univ, Yale Sch Environm, 195 Prospect St, New Haven, CT 06511 USA
[7] Yale Univ, Yale Ctr Nat Carbon Capture YCNCC, POB 208109, New Haven, CT 06520 USA
[8] Woodwell Climate Res Ctr, 149 Woods Hole Rd, Falmouth, MA 02540 USA
基金:
巴西圣保罗研究基金会;
关键词:
Soil organic matter;
Tropical conditions;
Subsoil carbon;
Agricultural intensification;
ORGANIC-MATTER;
MATO-GROSSO;
VERTICAL-DISTRIBUTION;
SUBSOIL HORIZONS;
STOCKS;
FOREST;
MANAGEMENT;
SEQUESTRATION;
STABILIZATION;
DEFORESTATION;
D O I:
10.1016/j.agee.2024.109451
中图分类号:
S [农业科学];
学科分类号:
09 ;
摘要:
Land-use change and agricultural intensification drive the widespread and relatively rapid decline of carbon (C) stocks in surface soils of the Amazon-Cerrado transition region of Brazil. However, less is known about C changes in deep-soil profiles. To understand the carbon dynamics in deep soils affected by land-use change and agricultural intensification, we sampled soil up to 800 cm beneath native forest (NV), minimum tillage soybean (S), soybean-maize (SM) cropland, old pasture (OP), and recently deforested land (RD) that was maintained as cleared but not cropped. All sampling took place at Fazenda Tanguro in Mato Grosso, Brazil. We determined soil C concentrations, mineral-associated organic matter (MAOM), particulate organic matter (POM), delta 13C, and water-extractable C (WEC). Soil C stocks to 800 cm ranged from 168.4 Mg ha-1 to 288.3 Mg ha-1. Regardless of the land use, the top 100 cm contained 30-40 % of the C stock to 800 cm, and about 50 % of all soil C stocks was concentrated until 300 cm. Conversion of forest to no-till single-cropping soybean negatively impacted soil C until 100 cm through reduction of MAOM stocks. The WEC concentrations were highest at the surface and decreased with depth. The RD showed the lowest WEC concentrations in the topsoil layer. Production intensification on the cropland led to superficial soil C accrual. Pasture showed great potential to store C through POM inputs on subsoil. This study provides important insights into the dynamics of carbon profiles in deep soils following land-use change and agricultural intensification. Thus, we can highlight: 1) Removal of native vegetation promotes rapid changes in surface C dynamics (less than 100 cm), consequently impacting C pools up to at least 300 cm in depth; 2) Intensification through double cropping has the potential to promote the restoration of these productive C pools over time; 3) as expected, soil C storage is closely related to clay content. Finally, based on these findings, we recommend that studies related to the impacts of agricultural expansion and intensification on the dynamics of soil C pools should focus efforts on sampling at least 100 cm deep in the soil, with stratified collections each 10 cm in the surface layers (up to 50 cm), and extend it to at least 300 cm, considering more areas, soil types, soil attributes, and land uses.
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页数:13
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