3. results – cont

1
3. Results – cont. 3. Results 1. Introduction and objectives 1. Introduction and objectives Pre-harvest Tree and Vine Biomass in a Forest in NW Mato Pre-harvest Tree and Vine Biomass in a Forest in NW Mato Grosso, Brazil Grosso, Brazil Ted R. Feldpausch (1)*, Stefan Jirka (1), Susan Riha (1), Carlos A. Passos (2), Johannes Lehmann (1), Franklin Jasper (3), Maria Jose Miranda de Souza Noquelli (2), Pericles de Aquino Botelho (2), Daniela Pauletto (2), Elenara Gandini (2), Erick C.M. Fernandes (1) (1) Cornell University, Ithaca, NY USA (2) Universidade Federal de Mato Grosso, Cuiabá, Brazil (3) Rohden Lignea Ltda, Juruena, Brazil; *[email protected] Universidade Federal de Mato Grosso Figure 2: Rohden forest (red) and the 1000 ha study site (yellow), Juruena, MT Brazil (image source Salatiel Alves de Araujo) b . Figure 1: a) forest cover in MT state, Brazil and study site location in NW Mato Grosso (MT), Brazil (S 10 25’ 29.7; W 58 45’ 34.9) . a . 2. Methods •The study site is a 25,000 ha primary forest in the municipality of Juruena, Brazil (Figure 1b). •The forest, privately owned and managed by Rohden Lignea Ltda forest, is selectively logged at a rate of 1000 ha yr -1 (Figure 2). •Annual rainfall is 2,200 mm with a strong dry season from June to September. •The soils are classified as Ultisols and Oxisols, are deep, acidic, and infertile. •Biomass estimates were made from: •1) a forest timber inventory of trees ≥30 cm diameter at breast height (DBH). •2) transects to inventory all trees ≥ 10 cm DBH and all vines. Commercial Timber Inventory (CTI) •A 100% pre-logging inventory was conducted for all commercially harvestable trees ≥30 cm DBH in a 1000 ha management unit (Figure 2). •Mapped, measured DBH, bole height, and species. Transects •To more intensively compare pre- and post- logging biomass and forest structure, we used these maps to locate 9 long (10x1000 m) and 8 short (10x200 to 500 m) stratified sampling transects within the management units •Measured DBH of all stems ≥10 cm DBH, lower and upper canopy height, species, and location to 10 cm on an x-y grid. •In nested transects (2x1000 m) within the transects we measured DBH of all vines and location on an x-y grid and calculated biomass (Gerwing and Farias 2000). •We are currently measuring soils to 60 cm depth at 25 m increments along the transects. Selective logging has become a common land-use in Brazilian Amazônia. As part of a larger study to evaluate the effect of reduced impact logging on C dynamics and nutrient stocks, forest structure, and forest regeneration potential, we conducted a pre-harvest campaign to estimate tree and vine biomass in a parcel of forest managed by Rohden Lignea Ltda in northwestern Mato Grosso (MT) (Figure 1a,b). Commercial timber inventory (CTI) (16600 stems 30 DBH) •Commercial biomass, 48 ± 77 Mg ha - 1 , was highly variable in the 1000 ha (Figure 3a). •Mean DBH of the CTI was 59 ± 24 cm. •Commercial bole height averaged 13 ± 3 m. •The 50 DBH class had the most stems. •Stem density averaged 11 ± 12 stem ha -1 (Figure 3b) . 1km Transect data (all trees 10 and vines) •Total tree and vine biomass averaged 319 Mg ha -1 (Table 1; Figure 4 and 5). •Vine stem density varied greatly (40%) across the forest (Table 1; Figure 6). •Tree stems in the 10-30 cm DBH class made up 84% of the total stems and 32% of the overall biomass (Table 1; Figure 6). •Biomass of the large diameter ≥60 cm DBH trees was more variable than small trees. •Tree height for trees ≥60 cm DBH averaged 33 m. •Two common species, Amescla and Breu, contributed 16% of the total biomass and 37% of the stems Figure 5: Tree and vine biomass in 200-1100 m long transects totaling 11.1 ha in a 1000 ha management block, Rohden Forest, Brazil. Columns with zero values for vines had no data. Tree and vine biom ass by transect 0 50 100 150 200 250 300 350 400 B 1-P3 B 2-F B 3-E B 4-E S-P17 U T10-P9 U T1-P22 U T2-P5 U T3-P19 U T3-P8 U T4-P8 U T5-P15 U T6-P 22 U T6-P8 U T8-P1 U T8-P17 U T9-P 17 M ean Transect biom ass [M g ha -1 ] V ine biom ass Tree ≥60 cm DBH Tree 30-60 cm DBH Tree 10-30 cm DBH Tree and vine stem density by transect 0 100 200 300 400 500 600 700 800 B1-P3 B2-F B3-E B4-E S-P17 U T10-P 9 U T1-P 22 U T2-P 5 U T3-P 19 U T3-P 8 U T4-P 8 U T5-P 15 U T6-P 22 U T6-P 8 U T8-P 1 U T8-P 17 U T9-P 17 M ean Transect stem density [no. ha -1 ] Tree stem s/ha V ine stem s/ha Figure 6: Tree and vine stem density in 200-1100 m long transects totaling 11.1 ha in Rohden Forest, Brazil. Columns with zero values for vines had no data. Note: vine values x0.1 A rea sam pled vs biom ass estim ate (M g ha -1 ) y = -54.258x + 322.75 R 2 = 0.1152 0 50 100 150 200 250 300 350 400 0 0.2 0.4 0.6 0.8 1 1.2 1.4 A rea (ha) B iom ass (M g ha -1 ) Figure 7: Area sampled versus biomass estimate for 17 transects in Rohden Forest, Brazil. 5. Acknowledgements We thank Pro-natura for logistical assistance and Rohden Lignea Industria for field support within the forest. Research was funded by the Large-scale Biosphere-Atmosphere Experiment in the Amazon (LBA- Eco) (ND-11) and an U.S. Environmental Protection Agency research fellowship to T.R. Feldpausch. 4.Discussion and Conclusions •Commercial timber represents 16% of the total biomass ≥10 cm DBH. •The ≥30 cm CTI underestimates tree biomass because it does not include non-commercial species nor trees within 50 m of streams. •Area sampled (0.2 to 1.2 ha) had no strong influence on biomass estimates (Figure 7). •The high biomass contribution from the 10-30 cm DBH class (32%) indicates the importance of including this class in biomass estimates (Table 1). •Our results indicate vine biomass is not insignificant (4.6% of the total biomass). This estimate is often lacking from forest biomass estimates. •We are using geostatistical analysis to determine the relationship between undisturbed forest biomass and structure, and soil and topographic landscape features. •Based on this analysis, we plan to estimate tree biomass as a function of DBH size classes, as well as vine biomass, over a larger area of the forest. Table 1: Mean biomass, percent biomass of the total, stem density, and percent density of the total by DBH class for transects totaling 11.1 ha in Rohden Tree Biom ass Tree Density Vine Biom ass Vine Density D B H C lass M g ha -1 % total no.ha -1 % total M g ha -1 no.ha -1 10 to <30 98 32 476 84 ≥30 to <60 111 36 74 13 ≥60 96 32 14 3 Total 304 563 15 2226 Table 2: Mean biomass, percent biomass of the total, stem density, and percent density of the total by DBH class for two common non-commercial species Amescla (Trattinickia burserifolia (Mart.) Willd.) and Breu (Protium heptaphyllum (Aubl.) March.), both Burseraceae, for transects totaling 11.1 ha in Biom ass Stem Density D B H C lass M g ha -1 % total stem s ha -1 % total 10 to <30 20 7 91 16 30 to <60 28 9 21 4 ≥60 0 0 0 0 Species sub-total 48 16 112 37 Overall- total 304 563 Figure 4: a) Vines contribute 15 Mg ha -1 to forest biomass, 2) DBH measurements for all trees ≥10 DBH (304 Mg ha -1 ). Figure 3: Contour and shaded surface maps for commercial timber trees ≥30 cm DBH a) biomass [Mg ha -1 ], b) stem density [no. ha -1 ]. 0 50 100 150 200 250 300 350 400 450 500 550 600 650 700 0 5 10 15 20 25 30 35 40 45 50 55 60 0 50 100 150 200 250 300 350 400 450 500 550 600 650 700 750 Figure 3a. 3b.

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Figure 5: Tree and vine biomass in 200-1100 m long transects totaling 11.1 ha in a 1000 ha management block, Rohden Forest, Brazil. Columns with zero values for vines had no data. Figure 3a. a. b. - PowerPoint PPT Presentation

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Page 1: 3. Results – cont

3. Results – cont.

3. Results1. Introduction and objectives1. Introduction and objectives

Pre-harvest Tree and Vine Biomass in a Forest in NW Mato Grosso, BrazilPre-harvest Tree and Vine Biomass in a Forest in NW Mato Grosso, BrazilTed R. Feldpausch (1)*, Stefan Jirka (1), Susan Riha (1), Carlos A. Passos (2),

Johannes Lehmann (1), Franklin Jasper (3), Maria Jose Miranda de SouzaNoquelli (2), Pericles de Aquino Botelho (2), Daniela Pauletto (2),

Elenara Gandini (2), Erick C.M. Fernandes (1)

(1) Cornell University, Ithaca, NY USA(2) Universidade Federal de Mato Grosso, Cuiabá, Brazil

(3) Rohden Lignea Ltda, Juruena, Brazil; *[email protected]

Universidade Federal de Mato Grosso

Figure 2: Rohden forest (red) and the 1000 ha study site (yellow), Juruena, MT Brazil (image source Salatiel Alves de Araujo)

b.

Figure 1: a) forest cover in MT state, Brazil and study site location in NW Mato Grosso (MT), Brazil (S 10 25’ 29.7; W 58 45’ 34.9) .

a.

2. Methods•The study site is a 25,000 ha primary forest in the municipality of Juruena, Brazil (Figure 1b).•The forest, privately owned and managed by Rohden Lignea Ltda forest, is selectively logged at a rate of 1000 ha yr-1 (Figure 2).•Annual rainfall is 2,200 mm with a strong dry season from June to September.•The soils are classified as Ultisols and Oxisols, are deep, acidic, and infertile.•Biomass estimates were made from:

•1) a forest timber inventory of  trees ≥30 cm diameter at breast height (DBH).•2) transects to inventory all trees ≥ 10 cm DBH and all vines.

Commercial Timber Inventory (CTI)•A 100% pre-logging inventory was conducted for all commercially harvestable trees ≥30 cm DBH in a 1000 ha management unit (Figure 2).

•Mapped, measured DBH, bole height, and species.

•We calculated commercial biomass, stem density, and basal area for 50x50 m cells (Brown eq. 3.2.3).•Using kriging interpolation, we generate contour and 3D shaded relief maps for the area (Figure 3).

Transects•To more intensively compare pre- and post-logging biomass and forest structure, we used these maps to locate 9 long (10x1000 m) and 8 short (10x200 to 500 m) stratified sampling transects within the management units

•Measured DBH of all stems ≥10 cm DBH, lower and upper canopy height, species, and location to 10 cm on an x-y grid.

•In nested transects (2x1000 m) within the transects we measured DBH of all vines and location on an x-y grid and calculated biomass (Gerwing and Farias 2000).•We are currently measuring soils to 60 cm depth at 25 m increments along the transects.

Selective logging has become a common land-use in Brazilian Amazônia. As part of a larger study to evaluate the effect of reduced impact logging on C dynamics and nutrient stocks, forest structure, and forest regeneration potential, we conducted a pre-harvest campaign to estimate tree and vine biomass in a parcel of forest managed by Rohden Lignea Ltda in northwestern Mato Grosso (MT) (Figure 1a,b).

Commercial timber inventory (CTI) (16600 stems ≥30 DBH)

•Commercial biomass, 48 ± 77 Mg ha-1, was highly variable in the 1000 ha (Figure 3a).•Mean DBH of the CTI was 59 ± 24 cm.•Commercial bole height averaged 13 ± 3 m.•The 50 DBH class had the most stems.•Stem density averaged 11 ± 12 stem ha-1 (Figure 3b).

1km Transect data (all trees ≥10 and vines)

•Total tree and vine biomass averaged 319 Mg ha-1 (Table 1; Figure 4 and 5).•Vine stem density varied greatly (40%) across the forest (Table 1; Figure 6).•Tree stems in the 10-30 cm DBH class made up 84% of the total stems and 32% of the overall biomass (Table 1; Figure 6).•Biomass of the large diameter ≥60 cm DBH trees was more variable than small trees.•Tree height for trees ≥60 cm DBH averaged 33 m.•Two common species, Amescla and Breu, contributed 16% of the total biomass and 37% of the stems (Table 2).

Figure 5: Tree and vine biomass in 200-1100 m long transects totaling 11.1 ha in a 1000 ha management block, Rohden Forest, Brazil. Columns with zero values for vines had no data.

Tree and vine biomass by transect

050

100150200250300350400

B1-

P3

B2-

FB

3-E

B4-

ES

-P17

UT1

0-P

9U

T1-P

22U

T2-P

5U

T3-P

19U

T3-P

8U

T4-P

8U

T5-P

15U

T6-P

22U

T6-P

8U

T8-P

1U

T8-P

17U

T9-P

17M

ean

Transect

biom

ass

[Mg

ha-1

]

Vine biomassTree ≥60 cm DBHTree 30-60 cm DBHTree 10-30 cm DBH

Tree and vine stem density by transect

0

100

200

300

400

500

600

700

800

B1-

P3

B2-

F

B3-

E

B4-

E

S-P

17

UT1

0-P

9

UT1

-P22

UT2

-P5

UT3

-P19

UT3

-P8

UT4

-P8

UT5

-P15

UT6

-P22

UT6

-P8

UT8

-P1

UT8

-P17

UT9

-P17

Mea

n

Transect

stem

den

sity

[no.

ha-1

]

Tree stems/haVine stems/ha

Figure 6: Tree and vine stem density in 200-1100 m long transects totaling 11.1 ha in Rohden Forest, Brazil. Columns with zero values for vines had no data. Note: vine values x0.1

Area sampled vs biomass estimate (Mg ha-1)

y = -54.258x + 322.75R2 = 0.1152

0

50

100

150

200

250

300

350

400

0 0.2 0.4 0.6 0.8 1 1.2 1.4

Area (ha)

Biom

ass

(Mg

ha-1

)

Figure 7: Area sampled versus biomass estimate for 17 transects in Rohden Forest, Brazil.

5. AcknowledgementsWe thank Pro-natura for logistical assistance and Rohden Lignea Industria for field support within the forest. Research was funded by the Large-scale Biosphere-Atmosphere Experiment in the Amazon (LBA-Eco) (ND-11) and an U.S. Environmental Protection Agency research fellowship to T.R. Feldpausch.

4.Discussion and Conclusions•Commercial timber represents 16% of the total biomass ≥10 cm DBH.•The ≥30 cm CTI underestimates tree biomass because it does not include non-commercial species nor trees within 50 m of streams.•Area sampled (0.2 to 1.2 ha) had no strong influence on biomass estimates (Figure 7).•The high biomass contribution from the 10-30 cm DBH class (32%) indicates the importance of including this class in biomass estimates (Table 1).•Our results indicate vine biomass is not insignificant (4.6% of the total biomass). This estimate is often lacking from forest biomass estimates.•We are using geostatistical analysis to determine the relationship between undisturbed forest biomass and structure, and soil and topographic landscape features.•Based on this analysis, we plan to estimate tree biomass as a function of DBH size classes, as well as vine biomass, over a larger area of the forest.

Table 1: Mean biomass, percent biomass of the total, stem density, and percent density of the total by DBH class for transects totaling 11.1 ha in Rohden Forest.

Tree

Biomass Tree

Density Vine

Biomass Vine

Density

DBH Class Mg ha-1 %

total no. ha-1 %

total Mg ha-1 no. ha-1 10 to <30 98 32 476 84 ≥30 to <60 111 36 74 13 ≥60 96 32 14 3 Total 304 563 15 2226

Table 2: Mean biomass, percent biomass of the total, stem density, and percent density of the total by DBH class for two common non-commercial species Amescla (Trattinickia burserifolia (Mart.) Willd.) and Breu (Protium heptaphyllum (Aubl.) March.), both Burseraceae, for transects totaling 11.1 ha in Rohden Forest.

Biomass Stem Density DBH Class Mg ha-1 % total stems ha-1 % total 10 to <30 20 7 91 16 30 to <60 28 9 21 4 ≥60 0 0 0 0 Species sub-total

48 16 112 37

Overall-total

304 563

Figure 4: a) Vines contribute 15 Mg ha-1 to forest biomass, 2) DBH measurements for all trees ≥10 DBH (304 Mg ha-1).

Figure 3: Contour and shaded surface maps for commercial timber trees ≥30 cm DBH a) biomass [Mg ha-1], b) stem density [no. ha-1].

050100150200250300350400450500550600650700

051015202530354045505560

050100150200250300350400450500550600650700750

Figure 3a.

3b.