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Characterizing Forest Degradation using
Multiple SAR Approaches: Case Study of Tropical
Peatland Forests in Sumatera, Indonesia
Arief Wijaya, Ari Susanti, Wahyu Wardhana, Sigit D. Sasmito, Serge
C. Rafanoharana, Gilang Aria Seta, Oka Karyanto and Louis Verchot
CIFOR on Forest Biomass
Monitoring: SWAMP
 Ecosystem carbon stocks and GHG emission
assessment on tropical wetlands
(mangroves and peatlands)
 cifor.org/swamp
 carbonstock.cifor.org
Forest Degradation using
Multiple SAR Approaches
 Study area: Kampar Peninsular, Sumatra
 Data used:
• quad-polarimetric ALOS PALSAR (May 2010)
• Landsat 5 TM (February 2010)
Field Data Preparation
Land use
Volume
(m3/ha)
AGB
(Mg/ha)
Carbon stocks
(MgC/ha)
Tree
height
(m)
Basal area
(m2)
LAI
Peat swamp
forest
592.35 228.25 114.12 16.92 33.19 2.96
Pioneer species
(Macaranga sp.)
32.63 7.47 3.74 11.22 9.71 3.09
Mangrove forest 182.16 105.65 52.82 9.53 11.79 2.38
Plantation forest 196.33 130.95 65.48 12.57 13.22 1.32
Rubber
plantation
125.73 113.44 56.72 14.95 51.02 2.06
SAR Data Preprocessing
 Data calibration, correction and noise filtering
 Polarimetric features: entropy, anisotropy and alpha angle
 Supervised classification: Multi-Layer Perceptron Neural Network
(MLP-NN) method and Maximum Likelihood Classification (MLC)
SAR Polarimetric
Features
1
2
3
4
5
6
7
8
9
SAR Classification Results
Conclusion
 This study shows an attempt to test multi
SAR approaches for characterizing forest
degradation event in tropical peat swamp
forests,
 L-Band of quad-polarimetric SAR data may
provide useful information to characterize
forest degradation,
 MLP-NN classification is more sensitive to
redundant input data, therefore the highest
accuracy (79.9%) was achieved applying
radar backscatter and multi-spectral
Landsat bands in the classification.
 Further study: feature selection of input
data on MLP-NN classification would benefit
for increasing the classification
accuracy
Further Question ??
Arief Wijaya Ph.D
Post-doctoral Research
Fellow
Contact:
CIFOR Headquarters
Jalan CIFOR Situ Gede
Bogor 16115 Indonesia
Tel: +62-251-8622622
Fax: +62-251-8622100
Email: a.wijaya@cgiar.org
Or
Sigit D. Sasmito
Email: s.sasmito@cgiar.org
Characterizing Forest Degradation using Multiple SAR Approaches
Acknowledgment
This work is conducted within Global Comparative Study on REDD+
Project initiated by Center for International Forestry Research (CIFOR).
The field measurement data was acquired by colleagues from Gadjah
Mada University,Yogyakarta, Indonesia, A.S, W.W and O.K, and therefore
we thank them to make the data available for this study.
References
[1] A. Luckman, et al., "A study of the relationship between radar backscatter and regenerating tropical forest biomass for
spaceborne SAR instruments," Remote Sensing of Environment, vol. 60, pp. 1-13, April 1997 1996.
[2] T. M. Kuplich, et al., "Relating SAR image texture to the biomass of regenerating tropical forests," International Journal
of Remote Sensing, vol. 26, pp. 4829-4854, 2005.
[3] J. E. S. Fransson and H. Israelsson, "Estimation of stem volume in boreal forests using ERS-1 C- and JERS-1 L-band
SAR data," International Journal of Remote Sensing, vol. 20, pp. 123-137, 1999.
[4] I. Hajnsek, et al., "INDREX II - Indonesian airborne radar experiment campaign over tropical forest in L- and P-band:
First results," in International Geoscience and Remote Sensing Symposium (IGARSS), Seoul, 2005, pp. 4335-4338.
[5] M. Isola and S. R. Cloude, "Forest height mapping using space-borne polarimetric SAR interferometry," in International
Geoscience and Remote Sensing Symposium (IGARSS), Sydney, NSW, 2001, pp. 1095-1097.
[6] S. Kingsley and S. Quegan, Understanding radar systems, 1st Edition ed.: SciTech Publishing, 1992.
[7] S. S. Saatchi, et al., "Mapping deforestation and land use in amazon rainforest by using SIR-C imagery," Remote
Sensing of Environment, vol. 59, pp. 191-202, 1997.
[8] Y. Rauste, "Multi-temporal JERS SAR data in boreal forest biomass mapping," Remote Sensing of Environment, vol. 97,
pp. 263-275, 2005.
[9] A. Luckman, et al., "A study of the relationship between radar backscatter and regenerating tropical forest biomass for
spaceborne SAR instruments," Remote Sensing of Environment, vol. 60, pp. 1-13, 1997.
[10] K. J. Ranson, et al., "Mapping of boreal forest biomass from spaceborne synthetic aperture radar," Journal of
Geophysical Research D: Atmospheres, vol. 102, pp. 29599-29610, 1997.
[11] E. Rignot, et al., "Mapping deforestation and secondary growth in Rondonia, Brazil, using imaging radar and thematic
mapper data," Remote Sensing of Environment, vol. 59, pp. 167-179, 1997.
[12] Wahyunto, et al., Distribution of Peatlands and Carbon Stocks in Sumatera and Kalimantan (In Indonesian). Bogor:
Wetlands International - Indonesia Programme and Wildlife Habitat Canada, 2005.
[13] A. Dermawan, et al., "Decentralization in Indonesia’s forestry sector – Is it over? What comes next?," in the Eleventh
Biennial Global Conference of The International Association for the Study of Common Property (IASCP) on the theme
‘Survival of the Commons: Mounting Challenges and New Realities’, Denpasar, Bali, 2006.

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Characterizing Forest Degradation using Multiple SAR Approaches

  • 1. Characterizing Forest Degradation using Multiple SAR Approaches: Case Study of Tropical Peatland Forests in Sumatera, Indonesia Arief Wijaya, Ari Susanti, Wahyu Wardhana, Sigit D. Sasmito, Serge C. Rafanoharana, Gilang Aria Seta, Oka Karyanto and Louis Verchot
  • 2. CIFOR on Forest Biomass Monitoring: SWAMP  Ecosystem carbon stocks and GHG emission assessment on tropical wetlands (mangroves and peatlands)  cifor.org/swamp  carbonstock.cifor.org
  • 3. Forest Degradation using Multiple SAR Approaches  Study area: Kampar Peninsular, Sumatra  Data used: • quad-polarimetric ALOS PALSAR (May 2010) • Landsat 5 TM (February 2010)
  • 4. Field Data Preparation Land use Volume (m3/ha) AGB (Mg/ha) Carbon stocks (MgC/ha) Tree height (m) Basal area (m2) LAI Peat swamp forest 592.35 228.25 114.12 16.92 33.19 2.96 Pioneer species (Macaranga sp.) 32.63 7.47 3.74 11.22 9.71 3.09 Mangrove forest 182.16 105.65 52.82 9.53 11.79 2.38 Plantation forest 196.33 130.95 65.48 12.57 13.22 1.32 Rubber plantation 125.73 113.44 56.72 14.95 51.02 2.06
  • 5. SAR Data Preprocessing  Data calibration, correction and noise filtering  Polarimetric features: entropy, anisotropy and alpha angle  Supervised classification: Multi-Layer Perceptron Neural Network (MLP-NN) method and Maximum Likelihood Classification (MLC)
  • 8. Conclusion  This study shows an attempt to test multi SAR approaches for characterizing forest degradation event in tropical peat swamp forests,  L-Band of quad-polarimetric SAR data may provide useful information to characterize forest degradation,  MLP-NN classification is more sensitive to redundant input data, therefore the highest accuracy (79.9%) was achieved applying radar backscatter and multi-spectral Landsat bands in the classification.  Further study: feature selection of input data on MLP-NN classification would benefit for increasing the classification accuracy
  • 9. Further Question ?? Arief Wijaya Ph.D Post-doctoral Research Fellow Contact: CIFOR Headquarters Jalan CIFOR Situ Gede Bogor 16115 Indonesia Tel: +62-251-8622622 Fax: +62-251-8622100 Email: a.wijaya@cgiar.org Or Sigit D. Sasmito Email: s.sasmito@cgiar.org
  • 11. Acknowledgment This work is conducted within Global Comparative Study on REDD+ Project initiated by Center for International Forestry Research (CIFOR). The field measurement data was acquired by colleagues from Gadjah Mada University,Yogyakarta, Indonesia, A.S, W.W and O.K, and therefore we thank them to make the data available for this study.
  • 12. References [1] A. Luckman, et al., "A study of the relationship between radar backscatter and regenerating tropical forest biomass for spaceborne SAR instruments," Remote Sensing of Environment, vol. 60, pp. 1-13, April 1997 1996. [2] T. M. Kuplich, et al., "Relating SAR image texture to the biomass of regenerating tropical forests," International Journal of Remote Sensing, vol. 26, pp. 4829-4854, 2005. [3] J. E. S. Fransson and H. Israelsson, "Estimation of stem volume in boreal forests using ERS-1 C- and JERS-1 L-band SAR data," International Journal of Remote Sensing, vol. 20, pp. 123-137, 1999. [4] I. Hajnsek, et al., "INDREX II - Indonesian airborne radar experiment campaign over tropical forest in L- and P-band: First results," in International Geoscience and Remote Sensing Symposium (IGARSS), Seoul, 2005, pp. 4335-4338. [5] M. Isola and S. R. Cloude, "Forest height mapping using space-borne polarimetric SAR interferometry," in International Geoscience and Remote Sensing Symposium (IGARSS), Sydney, NSW, 2001, pp. 1095-1097. [6] S. Kingsley and S. Quegan, Understanding radar systems, 1st Edition ed.: SciTech Publishing, 1992. [7] S. S. Saatchi, et al., "Mapping deforestation and land use in amazon rainforest by using SIR-C imagery," Remote Sensing of Environment, vol. 59, pp. 191-202, 1997. [8] Y. Rauste, "Multi-temporal JERS SAR data in boreal forest biomass mapping," Remote Sensing of Environment, vol. 97, pp. 263-275, 2005. [9] A. Luckman, et al., "A study of the relationship between radar backscatter and regenerating tropical forest biomass for spaceborne SAR instruments," Remote Sensing of Environment, vol. 60, pp. 1-13, 1997. [10] K. J. Ranson, et al., "Mapping of boreal forest biomass from spaceborne synthetic aperture radar," Journal of Geophysical Research D: Atmospheres, vol. 102, pp. 29599-29610, 1997. [11] E. Rignot, et al., "Mapping deforestation and secondary growth in Rondonia, Brazil, using imaging radar and thematic mapper data," Remote Sensing of Environment, vol. 59, pp. 167-179, 1997. [12] Wahyunto, et al., Distribution of Peatlands and Carbon Stocks in Sumatera and Kalimantan (In Indonesian). Bogor: Wetlands International - Indonesia Programme and Wildlife Habitat Canada, 2005. [13] A. Dermawan, et al., "Decentralization in Indonesia’s forestry sector – Is it over? What comes next?," in the Eleventh Biennial Global Conference of The International Association for the Study of Common Property (IASCP) on the theme ‘Survival of the Commons: Mounting Challenges and New Realities’, Denpasar, Bali, 2006.

Editor's Notes

  • #2: Description: Picture: West Kalimantan tropical peatlands view from air borne
  • #3: Description: This slide is to highlight CIFOR research on tropical wetlands carbon stocks and GHG emission measurement (SWAMP activities)
  • #4: Description: This study focuses on peatland forest ecosystem at Kampar Peninsular, Sumatera, Indonesia, which is geographically located between 101°50’ E and 104°07’ E and between 0°10’ dan 1°14’ N (Figure 1) The Kampar Peninsula is a wetland forest consists of great numbers of natural resources. The area has a size of approximately 700,000 ha, and peatlands in this region are mostly covered with 2-layer forest canopies. Peatlands in this region have depth from 50 cm (very shallow) to more than 20 meter (very deep). The peatland forests in Kampar Peninsula cover 17% of total peatlands in Riau Province (4.044 million ha), and for the entire country this province covers 56% of total 20.5 million ha of peatlands in Indonesia [12].
  • #5: Description: From sampling plots data, we estimate 114 Mg/ha of carbon above ground biomass in the peatland forests, while the first pioneer species dominated with Macaranga sp. has very low carbon stocks of 3.7 Mg/ha. Mangrove forests and rubber plantation have relatively similar carbon stocks of ~50 Mg/ha. Carbon AGB increases following the increase of stand volume, but the LAI does not correspond directly with the AGB (Table 1), as pioneer species in general has higher LAI than other sampled peat forest environments.
  • #6: Description: One scene of quad-polarimetric ALOS PALSAR data acquired during the end of rain season on May 2010 and Landsat 5 Thematic Mapper (TM) from February 2010 are used to characterize forest degradation event. Calibration of radar backscatter and corrections to other topographic distortions were conducted. Noise filtering to reduce speckle effects is applied using Enhanced-Lee filter. Polarimetric features, i.e. entropy, anisotropy and alpha angle, were generated from the coherency matrices of polarimetric SAR data and plotted against training observation data over degraded peatlands, pristine peatland forest and other land uses to characterize the profiles of radar backscatter in discriminating different peat forests conditions. Polarimetric features: alpha angle (a), entropy (b) and anisotropy (c). Two additional polarimetric features were also calculated, PolSAR random volume over ground volume ratio (RVOG_mv) based on polarimetric data inversion and accumulation of polarimetric backscatter (span in decibel / span_db).
  • #7: Description: We used α/H (alpha angle - entropy) plane to plot ground truth data identified from the SAR data and the figure shows that except for water body and cleared land which are dominated by flat surface scattering (single bounce scattering), the vegetated land cover classes mainly show volume scattering due to random scattering from tree canopy cover. This may partly explain that low carbon biomass represented by low/sparse vegetation has more surface scattering, whereas moderate/higher carbon biomass may be identified from their volume scattering behavior. However, from Figure 2 we could not assess if the application of both polarimetric features could better discriminate different vegetation classes as many of the training data points are falling in the region 5, which characterize the domination of volume scattering mechanism. It has been already well-accepted that vegetation cover represents mainly volume scattering behavior, therefore to better classify different vegetation cover conditions, the use of radar backscatter (sigma nought) and other ancillary data are highly recommended.
  • #8: Description: This study found that MLP-NN outperformed MLC technique to classify different forest classes over tropical peatland ecosystem. We also find that for MLP-NN to achieve the highest classification accuracy, addition of redundant input on the classification model will not give contribute to improved accuracy. Whereas, the MLC technique has a trend of improved classification accuracy following the number of input data used in the classification. The formal agreement is that statistical classifier, such as MLC method may suffer from non-normal data distribution, however this study does not seem to show such cases. For MLP-NN classification, feature selection of input data that are useful for the classification would benefit for increasing the classification accuracy. These facts are unfortunately beyond the scope of the present study, and are interesting to further explore.
  • #9: Description: This study shows an attempt to test multi SAR approaches for characterizing forest degradation event in tropical peat swamp forests. We found L-Band of quad-polarimetric SAR data may provide useful information to characterize such event. Additionally, the accuracy of SAR classification depends mainly from variations of input data used for the classification, as well as the classification techniques being used. Applying MLC method, the SAR classification yielded 77.8% of accuracy combining radar backscatter, polarimetric features, RVOG_mv and span_db. While, MLP-NN classification is more sensitive to redundant input data, therefore the highest accuracy (79.9%) was achieved applying radar backscatter and multi-spectral Landsat bands in the classification.
  • #10: Description:
  • #11: Description: