219 - soil carbon stocks and dynamics in acre: …...tropical soils store 506 pg c, of these, around...

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219 - SOIL CARBON STOCKS AND DYNAMICS IN ACRE: CONTRASTS WITH THE REMAINING BRAZILIAN AMAZON Antonio Willian Flores de Melo 1 , Plínio Barbosa de Camargo 1 , Cleber Ibraim Salimon 1 , Eric A. Davidson 3 , Susan E. Trumbore 3 , Judson Ferreira Valentim 4 (1) Universidade de São Paulo, Centro de Energia Nuclear na Agricultura, [email protected] , [email protected] , [email protected] . (2) The Woods Hole Research Center, [email protected] . (3) University of California, Department of Earth System Science, [email protected] . (4) Empresa Brasileira de Pesquisa Agropecuária, Centro de Pesquisa Agroflorestal do Acre, [email protected] . INTRODUCTION METHODS RESULTS Soils are an important reservoir of carbon. It is considered that the first meter deep of the planet’s soils stores from 1300 to 2000 Pg C (1 Pg = 10 15 g). Tropical soils store 506 Pg C, of these, around 66 Pg C are in the soils of the Amazon and 47 Pg C in Brazilian legal Amazon. The State of Acre is located in the extreme west of Brazil, occupying an area that had great geological influence from the mountain chain of Andes. The soils present pedologic characteristics very different from the ones found in the remaining of Brazilian Amazon, prevailing Inceptisols, Alfisols, and Ultisols, generally eutrophic, young and little weathered, in some cases presents argilas 2:1. Not much is known about the impact of the use of the earth on the organic matter in these soil conditions. OBJECTIVES Estimate the stock of carbon of the main classes of soils of the State of Acre and to compare with studies carried out for the Amazon area. To evaluate the effect of the change in the use and covering of the earth on the stock of carbon and isotopic composition of the organic matter in two soil conditions in Acre. To reach the objectives the work was performed in two scales, regional and local. The first case estimated the stocks of carbon up to one meter deep, using a map of soils in the scale 1:1.000.000 and analytic data of pedologic profiles accomplished in the area (Figure 1). The second case determined the concentration of carbon, δ13C and density of the soil of samples collected at 12- 15, 20 year-old pasture lands, and forest in the depths 0-5, 5-10, 10-20, 20-30, 30-40, 50-60, 70-80 and 90-100 cm, in Ultisols (well drained) and Alfisols (poorly drained) (Figure 2). Figure 1 – Location of 182 profiles used to estimate soil carbon stock in the State of Acre. Figure 2 – Geographic location of studied areas where was the effect of changing land use/cover over the stock and the isotopic composition of soil carbon. Figures 3 and 4, and table 1 show results from estimates of soil carbon stocks in the main soil s of the State of Acre. Figures 5, 6 and 7 show the results of evaluations on the stocks of carbon isotopic composition in soils of pasture and primary forest in two farms in the East of the State of Acre. 100 80 60 40 20 0 depth (cm) (b) Cp Cf 0 5 10 15 20 soil organic carbon (Mg ha) 100 80 60 40 20 0 depth (cm) (a) 0 5 10 15 20 25 30 soil organic carbon (Mg C ha-1) 100 80 60 40 20 0 deepth (cm) (a) 40 30 20 10 0 deepth (cm) (b) FA (forest) FB (forest) P20A (20 yr old pasture) P20B (20 yr old pasture) P20 (20 yr old pasture) P15A (15 yr old pasture) P12B (12 yr old pasture) FA (forest) FB (forest) P20A (20 yr old pasture) P20B (20 yr old pasture) P20 (20 yr old pasture) P15A (15 yr old pasture) P12B (12 yr old pasture) -30 -28 -26 -24 -22 -20 -18 -16 -14 δ13C (‰) 100 80 60 40 20 0 depth (cm) FA (forest) FB (forest) P20A (20 yr old pasture) P20B (20 yr old pasture) P20 (20 yr old pasture) P15A (15 yr old pasture) P12B (12 yr old pasture) 0 20 40 60 80 100 C (Mg ha -1 ) 64 ± 2 69 ± 3 59 ± 2 55 ± 4 FA P15A P20A P20 (a) 0 20 40 60 80 100 C (Mg ha -1 ) 71 ± 3 87 ± 4 81 ± 5 FB P12B P20B (b) Figure 3 – Relative distribution of 6 main groups of soils based on the map of soils in the State of Acre – scale 1:1.000.000. Estimates of soil carbon stocks in the main soils of the Acre Table 1. Carbon stock (kg m-2) in the first 100 cm depth. Data cooperation. Figure 4 – Map of carbon stock in the soils in the State of Acre (Mg ha-1 to 100 cm depth). soil classes 0 10 20 30 40 50 percent of Acre area 40 % 24% 14 % 11 % 9 % 2 % Luvissolos (Alfisols) Cambissolos (Inceptisols) Argissolos (Ultisols) Alissolos (Alfisols) Solos Hidromórficos (Entisols) Latossolos (Oxisols) PERU BOLÍVIA PERU AMAZONAS AMAZONAS RODÔNIA 74°0'0"W 74°0'0"W 72°0'0"W 72°0'0"W 70°0'0"W 70°0'0"W 68°0'0"W 68°0'0"W 12°0'0"S 12°0'0"S 10°0'0"S 10°0'0"S 8°0'0"S 8°0'0"S Soil Carbon Stocks (Mg C ha-1 to 1 m depth) 55 - 60 61 - 65 66 - 70 71 - 75 30°0'0"S 30°0'0"S 0°0'0"N 0°0'0"N Area of Study 50 0 50 100 150 25 Kilometres Figure 5 Mean values and standard deviation of carbon stocks (kg m-2). Graphic (a) concentration of C up to 100 cm depth. Graphic (b) concentration of C up to 10 cm depth. Figure 6 – Carbon stock (Mg h-1) in the first 100 cm depth soil in studied areas. Graphic (a) areas over Ultisol, and Graphic (b) areas over Alfisol. Figure 7 – Variation of δ13C (‰) in soil with depth in the studied areas. Figure 8 – Carbon stock (Mg h-1) corresponding to Cf (forest derived carbon) and Cp (pasture derived carbon) in soil profile. Graphic (a) refers to data in the 20 yr old pasture over Ultisol, and Graphic (b) refers to data in the 20 yr old pasture over Alfisol. Evaluations on the stocks of carbon isotopic composition in soils of pasture and primary forest This work had as objectives: Embrapa Acre CONCLUSIONS Soils in Acre store about 1 Pg C to 1m depth. Eutrophic soils contain smaller C stocks than dystrophic soils within the same soil order. The rate of decomposition of carbon in Alfisols is lower than in Ultisols, but the mean residence time of organic matter is longer. The Ultisols tend to lose more carbon with land-use change. Based on soil carbon data, the productivity of Brachiaria brizantha cv. Marandu pastures is probably lower on Alfisols, indicating that, in addition to soil fertility, other characteristics such as soil drainage affect pasture productivity and arbon dynamics. C (kg m ) Soil Classification Acre ψ Brazilian Amazonia ¥ Amazon Basin # South America £ Luvissolos Crômicos 7,5 ± 1,1 Luvissolos Hipocrômicos 7,1 ± 1,4 7,6 ± 0,4 8,9 ± 34 4,0 Vertissolos Ebanicos 11,3 11,3 14,0 Cambissolos Háplicos Ta Eut. 5,9 ± 1,6 6,8 ± 1,1 Cambissolos Háplicos Ta Dist. 6,9 ± 1,5 7,7 ± 0,5 Cambissolos Háplicos Tb Dist. 6,4 ± 2,1 9,5 ± 46 60,0 Chernossolos Háplicos 8,9 ± 1,4 15,0 Argissolos Vermelhos Distófico 6,8 ± 1,4 Argissolos Amarelos Distróficos 5,8 ± 1,3 Argissolos Vermelho Amarelos Distróficos 6,1 ± 1,9 9,5 ± 0,3 8,5 ± 42 8,0 Nitossolos Háplicos Distróficos 5,9 ± 2.5 Nitossolos Vermelhos Distróficos 5,8 ± 1,0 15,0 ± 1,9 11.1 ± 34 Alissolos Crômicos 6,8 ± 1,3 Alissolos Hipocrômicos 7,8 ± 1,6 15,2 ± 45 Gleissolos Háplicos Ta Eutróficos 6,3 ± 2,1 7,2 ± 0,8 Gleissolos Háplicos Ta Distróficos 7,4 ± 3,7 12,2 ± 1,4 12,7 ± 59 Neossolos Fúvicos Ta Eutróficos 5,2 ± 1,0 6,8 ± 0,8 7,5 ± 46 Plintossolos Háplicos Ta Distróficos7,7 ± 1,4 Plintossolos Argilúvicos Ta Distróficos 6,6 ± 0,8 9,4 ± 0,9 6,1 ± 45 Latossolos Vermelhos Distróficos 5,9 ± 1,7 9,3 ± 0,8 10,2 ± 40 Latossolos Amarelos Distróficos 6,3 ± 2,1 8,5 ± 0,4 12,0 ψ Data of this work. £ Bohn, 1976. ¥ Moraes et al, 1995. Batjes & Dijkshoorn, 1999. #

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Page 1: 219 - SOIL CARBON STOCKS AND DYNAMICS IN ACRE: …...Tropical soils store 506 Pg C, of these, around 66 Pg C are in the soils of the Amazon and 47 Pg C in Brazilian legal Amazon. The

219 - SOIL CARBON STOCKS AND DYNAMICS IN ACRE: CONTRASTS WITH THE REMAINING BRAZILIAN AMAZON

Antonio Willian Flores de Melo1, Plínio Barbosa de Camargo1, Cleber Ibraim Salimon1, Eric A. Davidson3, Susan E. Trumbore3, Judson Ferreira Valentim4

(1) Universidade de São Paulo, Centro de Energia Nuclear na Agricultura, [email protected], [email protected], [email protected]. (2) The Woods Hole Research Center, [email protected]. (3) University of California, Department of Earth System Science, [email protected]. (4)

Empresa Brasileira de Pesquisa Agropecuária, Centro de Pesquisa Agroflorestal do Acre, [email protected].

INTRODUCTION

METHODS

RESULTS

Soils are an important reservoir of carbon. It is considered that the first meter deep of the planet’s soils stores from 1300 to 2000 Pg C (1 Pg = 1015 g). Tropical soils store 506 Pg C, of these, around 66 Pg C are in the soils of the Amazon and 47 Pg C in Brazilian legal Amazon. The State of Acre is located in the extreme west of Brazil, occupying an area that had great geological influence from the mountain chain of Andes. The soils present pedologiccharacteristics very different from the ones found in the remaining of Brazilian Amazon, prevailing Inceptisols, Alfisols, and Ultisols, generally eutrophic, young and little weathered, in some cases presents argilas 2:1. Not much is known about the impact of the use of the earth on the organic matter in these soil conditions.

OBJECTIVES

Estimate the stock of carbon of the main classes of soils of the State of Acre and to compare with studies carried out for the Amazon area.

To evaluate the effect of the change in the use and covering of the earth on the stock of carbon and isotopic composition of the organic matter in two soil conditions in Acre.

To reach the objectives the work was performed in two scales, regional and local. The first case estimated the stocks of carbon up to one meter deep, using a map of soils in the scale 1:1.000.000 and analytic data of pedologic profiles accomplished in the area (Figure 1). The second case determined the concentration of carbon, δ13C and density of the soil of samples collected at 12-15, 20 year-old pasture lands, and forest in the depths 0-5, 5-10, 10-20, 20-30, 30-40, 50-60, 70-80 and 90-100 cm, in Ultisols (well drained) and Alfisols (poorly drained) (Figure 2).

Figure 1 – Location of 182 profiles used to estimate soil carbon stock in the State of Acre.

Figure 2 – Geographic location of studied areas where was the effect of changing land use/cover over the stock and the isotopic composition of soil carbon.

Figures 3 and 4, and table 1 show results from estimates of soil carbon stocks in the main soil s of the State of Acre.

Figures 5, 6 and 7 show the results of evaluations on the stocks of carbon isotopic composition in soils of pasture and primary forest in two farms in the East of the State of Acre.

100

80

60

40

20

0

dept

h (c

m)

(b)

CpCf

0 5 10 15 20

soil organic carbon (Mg ha-2)

100

80

60

40

20

0

dept

h (c

m)

(a)

0 5 10 15 20 25 30

soil organic carbon (Mg C ha-1)

100

80

60

40

20

0

deep

th (c

m)

(a)

40

30

20

10

0

deep

th (c

m)

(b)

FA (forest)FB (forest)P20A (20 yr old pasture)P20B (20 yr old pasture)P20 (20 yr old pasture)P15A (15 yr old pasture)P12B (12 yr old pasture)

FA (forest)FB (forest)P20A (20 yr old pasture)P20B (20 yr old pasture)P20 (20 yr old pasture)P15A (15 yr old pasture)P12B (12 yr old pasture)

-30 -28 -26 -24 -22 -20 -18 -16 -14

δ13C (‰)

100

80

60

40

20

0

dept

h (c

m)

FA (forest)FB (forest)P20A (20 yr old pasture)P20B (20 yr old pasture)P20 (20 yr old pasture)P15A (15 yr old pasture)P12B (12 yr old pasture)

0

20

40

60

80

100

C (M

g ha

-1)

64 ± 2

69 ± 3

59 ± 255 ± 4

FAP15AP20AP20

(a)

0

20

40

60

80

100

C (M

g ha

-1)

71 ± 3

87 ± 4

81 ± 5

FBP12BP20B

(b)

Figure 3 – Relative distribution of 6 main groups of soils based on the map of soils in the State of Acre – scale 1:1.000.000.

Estimates of soil carbon stocks in the main soils of the Acre Table 1. Carbon stock (kg m-2) in the first 100 cm depth. Data cooperation.

Figure 4 – Map of carbon stock in the soils in the State of Acre (Mg ha-1 to 100 cm depth).

soil classes0

10

20

30

40

50

perc

ent o

f Acr

e ar

ea

40 %

24%

14 %11 %

9 %

2 %

Luvissolos (Alfisols)Cambissolos (Inceptisols)Argissolos (Ultisols)Alissolos (Alfisols)Solos Hidromórficos (Entisols)Latossolos (Oxisols)

PERU

BOLÍVIA

PERU

AMAZONAS

AMAZONAS

RODÔNIA

74°0'0"W

74°0'0"W

72°0'0"W

72°0'0"W

70°0'0"W

70°0'0"W

68°0'0"W

68°0'0"W

12°0'0"S 12°0'0"S

10°0'0"S 10°0'0"S

8°0'0"S 8°0'0"S

Soil Carbon Stocks(Mg C ha-1 to 1 m depth)

55 - 6061 - 6566 - 7071 - 75

30°0'0"S 30°0'0"S

0°0'0"N 0°0'0"N

Area of Study50 0 50 100 15025

Kilometres

Figure 5 – Mean values and standard deviation of carbon stocks (kg m-2). Graphic (a) concentration of C up to 100 cm depth. Graphic (b) concentration of C up to 10 cm depth.

Figure 6 – Carbon stock (Mg h-1) in the first 100 cm depth soil in studied areas. Graphic (a) areas over Ultisol, and Graphic (b) areas over Alfisol.

Figure 7 – Variation of δ13C (‰) in soil with depth in the studied areas.

Figure 8 – Carbon stock (Mg h-1) corresponding to Cf(forest derived carbon) and Cp (pasture derived carbon) in soil profile. Graphic (a) refers to data in the 20 yr old pasture over Ultisol, and Graphic (b) refers to data in the 20 yr old pasture over Alfisol.

Evaluations on the stocks of carbon isotopic composition in soils of pasture and primary forest

This work had as objectives:

Embrapa Acre

CONCLUSIONS

Soils in Acre store about 1 Pg C to 1m depth. Eutrophic soils contain smaller C stocks than dystrophic soils within the same soil order.

The rate of decomposition of carbon in Alfisols is lower than in Ultisols, but the mean residence time of organic matter is longer.

The Ultisols tend to lose more carbon with land-use change.

Based on soil carbon data, the productivity of Brachiaria brizantha cv. Marandu pastures is probably lower on Alfisols, indicating that, in addition to soil fertility, other characteristics such as soil drainage affect pasture productivity and arbon dynamics.

C (kg m-2)Soil Classification Acreψ Brazilian

Amazonia¥AmazonBasin#

SouthAmerica£

Luvissolos Crômicos 7,5 ± 1,1Luvissolos Hipocrômicos 7,1 ± 1,4 7,6 ± 0,4 8,9 ± 34 4,0

Vertissolos Ebanicos 11,3 11,3 14,0Cambissolos Háplicos Ta Eut. 5,9 ± 1,6 6,8 ± 1,1Cambissolos Háplicos Ta Dist. 6,9 ± 1,5 7,7 ± 0,5Cambissolos Háplicos Tb Dist. 6,4 ± 2,1

9,5 ± 46 60,0

Chernossolos Háplicos 8,9 ± 1,4 15,0Argissolos Vermelhos Distófico 6,8 ± 1,4Argissolos Amarelos Distróficos 5,8 ± 1,3Argissolos Vermelho Amarelos Distróficos

6,1 ± 1,9 9,5 ± 0,38,5 ± 42 8,0

Nitossolos Háplicos Distróficos 5,9 ± 2.5Nitossolos Vermelhos Distróficos 5,8 ± 1,0 15,0 ± 1,9 11.1 ± 34

Alissolos Crômicos 6,8 ± 1,3Alissolos Hipocrômicos 7,8 ± 1,6

15,2 ± 45

Gleissolos Háplicos Ta Eutróficos 6,3 ± 2,1 7,2 ± 0,8Gleissolos Háplicos Ta Distróficos 7,4 ± 3,7 12,2 ± 1,4 12,7 ± 59

Neossolos Fúvicos Ta Eutróficos 5,2 ± 1,0 6,8 ± 0,8 7,5 ± 46Plintossolos Háplicos Ta Distróficos7,7 ± 1,4Plintossolos Argilúvicos Ta Distróficos

6,6 ± 0,8 9,4 ± 0,9 6,1 ± 45

Latossolos Vermelhos Distróficos 5,9 ± 1,7 9,3 ± 0,8 10,2 ± 40Latossolos Amarelos Distróficos 6,3 ± 2,1 8,5 ± 0,4

12,0ψData of this work. £ Bohn, 1976. ¥Moraes et al, 1995. Batjes & Dijkshoorn, 1999.#