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Floresta e Ambiente

Print version ISSN 1415-0980On-line version ISSN 2179-8087

Floresta Ambient. vol.26 no.2 Seropédica  2019  Epub Apr 04, 2019

http://dx.doi.org/10.1590/2179-8087.063417 

Original Article

Forest Management

Selective Logging Detection in the Brazilian Amazon

Olívia Bueno da Costa1 
http://orcid.org/0000-0002-6739-8135

Eraldo Aparecido Trondoli Matricardi1 
http://orcid.org/0000-0002-5323-6100

Marcos Antonio Pedlowski2 
http://orcid.org/0000-0003-3949-8240

Eder Pereira Miguel1 
http://orcid.org/0000-0001-6259-4594

Ricardo de Oliveira Gaspar1 
http://orcid.org/0000-0002-2035-2180

1 Universidade de Brasilia – UNB, Brasília/DF, Brasil

2 Universidade Estadual do Norte Fluminense – UENF, Campos dos Goytacazes/RJ, Brasil

ABSTRACT

Selective logging activities are commonly observed in the Brazilian Amazon and are responsible for high forest impact. In this study, selective logging detection techniques and the spatiotemporal extension of forests impacted by logging activities between 2003 and 2014 in portions of the states of Mato Grosso, Pará, and Rondônia were assessed using remotely sensing data. Based on results obtained, it was estimated that the overall accuracies are greater than 91% for techniques applied to detect forests impacted by selective logging in the study areas. Forests impacted by selective logging increased in Western state of Mato Grosso and Northern state of Rondônia, which indicates a stage high forest activity in these regions. In contrast, in Eastern state of Pará, a decrease in forests impacted by logging activities was observed, which indicates collapsed stage of logging activities resulting from deforestation and predatory logging in that region.

Keywords:  Legal Amazon; geoprocessing and forest degradation

1. INTRODUCTION

Forest degradation in the Amazon has several consequences to ecological processes ( Koltunov et al., 2009 ; Andrade et al., 2014 ; Berenguer et al., 2014 ). Canopy openings left by selective logging activities combined with large amounts of organic matter from dead trees increases forest vulnerability to subsequent fires ( Uhl & Kauffman, 1990 ; Holdsworth & Uhl, 1997 ; Nepstad et al., 1998 ; Fearnside, 1999 ; Cochrane & Laurance, 2008 ).

Conventional selective logging results in greater impacts on forests as it removes timber species usually without proper planning and/or logging techniques. In contrast, selective logging uses several techniques that reduce forest damage and shorten the forest recovery period based on the detailed planning of logging activities ( Putz et al., 2012 ; West et al., 2014 ).

Forest degradation as a result of selective logging activities, especially by conventional logging, causes the release of substantial amounts of carbon into the atmosphere ( Huang & Asner, 2010 ; Berenguer et al., 2014 ). In the period between 2007 and 2013, selective logging activities and forest fires accounted for 47% (gross average of emissions) of deforestation that took place in the same period in the Amazon ( Aguiar et al., 2016 ).

The detection of high-intensity selective logging in Amazon forests is fundamental for the analysis and the understanding of the spatial distribution of forest degradation, and to support the study of current climate changes and deforestation. Based on the above, remotely sensing imagery is a crucial data source for mapping selective logging in dense and inaccessible Amazon areas, since it allows a broad view and quick coverage of the area of interest ( Souza et al., 2005 ; Anwar & Stein, 2012 ) at low cost ( Nepstad et al., 1999 ).

Different mapping techniques to detect forests degraded by selective logging activities in the Legal Amazon are described in literature, such as visual interpretation, spectral mixture analysis, texture filter, CLASlite, as well as radar and Lidar detectors ( Asner et al., 2005 ; Matricardi et al., 2010 ; Keller et al., 2012 ; Souza et al., 2013 ; Andersen et al., 2014 ; Joshi et al., 2015 ; INPE, 2016 ). However, such studies have focused on the temporal assessment or spatial dimension of forest degradation.

The aim of this study was to assess the accuracy of selective logging detection techniques used in the Amazon, especially in areas of forests submitted to legal and illegal conventional selective logging. This study also sought to estimate areas of selectively logged forests in sites spatially located in the states of Mato Grosso, Pará, and Rondônia. These results can be used for developing and applying remote sensing techniques to assess forest impacts in the Amazon.

2. METHODS

The study sites comprised three states of the Brazilian Legal Amazon: Mato Grosso (municipalities of Santa Carmen, Nova Ubiratã, and Feliz Natal), Pará (municipalities of Paragominas, Goianésia do Pará, Dom Eliseu, and Ulianópolis) and Rondônia (municipality of Porto Velho), spatially located within five Landsat 5 (TM) and Landsat 8 (OLI) scenes ( Figure 1 ) ( Table 1 ).

Figure 1 Study area and Landsat and Rapid Eye images used to assess the accuracy of the selective logging mapping technique.  

Table 1 Landsat and Rapid Eye images acquired in 2014 used to assess the accuracy of the selective logging classification.  

Satellite/Sensor Mato Grosso Pará Rondônia
Scene Date Scene Date Scene Date
Landsat
(OLI)
226/68 Oct 23 223/62 Dec 21 232/66 Oct 1
226/69 Aug 20 223/63 Dec 21
RapidEye 2133426 May 6 2237328 June 26 2035216 June 24
2133527 May 6 2237427 June 26 2035215 June 24
2133427 July 5 2237428 June 26
2133526 July 5 2237327 June 26
2133525 May 1
2133425 Aug 13

Landsat scenes were radiometrically corrected for physical values at the Top Of the Atmosphere (TOA) reflectance ( Chander et al., 2009 ) using ENVI® 5.0. Subsequently, Landsat scenes were georeferenced using Datum WGS 84 Datum and UTM projection system. Image georeferencing was conducted using six control points from an orthorectified image (acquired from the US Geological Survey - USGS) and images acquired from the INPE (Institute of Space Research) website. The six control points were used for image rectification by applying the first-order polynomial and nearest neighbor re-sampling technique. Individual image geometric correction was only accepted if RMS value was lower than 0.5 pixels ( Dewa & Danoedoro, 2017 ).

The methodology ( Figure 2 ) was based on applying a semiautomatic technique that combined texture algorithm for detecting log-landing patios and eye-inspection to map selectively logged forests, showing obvious forest degradation through Landsat-5 TMimages (acquired in 2003, 2006, and 2010) and Landsat-8 OLI images (acquired in 2014). Forest and non-forest mask was created from PRODES (Monitoring of the Brazilian Amazonian Forest by Satellite) deforestation dataset to mask out “deforestation” lands, since this study was focused on forested areas only. A buffer zone of 180 m corresponding to area impacted by selective logging activities was built around detected log-landing patios. This buffer zone was defined based on field measurements conducted by Matricardi et al. (2010) and applied in this study ( Figure 2 ).

Figure 2 Flow diagram for the selective semi-automated logging detection technique using Landsat Imagery.  

Confusion matrix was used to estimate the overall accuracy, commission and omission errors, producer and user accuracies of the selective logging mapping technique applied on five Landsat images acquired in 2014 ( Congalton & Green, 2008 ).

The classification conducted on the Landsat imagery was eye-inspected on a computer screen using twelve high spatial resolution (5m) Rapid Eye satellite images. Additional observations related to the spectral patterns of selective logging on satellite images were carried out during fieldwork conducted in November 2016 in the states of Mato Grosso (municipality of Feliz Natal) and Rondônia (municipality of Porto Velho).

Six Rapid Eye satellite images were used for the study site in the state of Mato Grosso ( Figure 1 , Table 1 ). A polygon including the six Rapid Eye images was built and 260 points were randomly distributed within the polygon adopting minimum distance of 500 meters from each other. This procedure ensured that the random sampling points were more efficiently distributed throughout the study area. Dates the closest as possible between Landsat-8 and Rapid Eye images were searched to reduce seasonal effects on satellite images.

Finally, points randomly sampled distributed over the study site were used to observe evidence of selective logging on Rapid Eye images. Based on visual evidences of selective logging observed on Rapid Eye images, each sampled point was classified either as selectively logged forest or not logged forest and compared to classification based on two Landsat 8 images (Path/Row226/68 and 226/69) in the state of Mato Grosso.

Four Rapid Eye images were used ( Figure 1 , Table 1 ) in the state of Pará. The previously described methodological procedures were adopted to assess selective logging classification accuracy in Pará. A total of 200 sample points were randomly distributed within Rapid Eye images and compared to classification based on Landsat 8 images 223/62 and 223/63.

Similarly, two Rapid Eye images were used ( Figure 1 , Table 1 ) in the state of Rondônia. A total of 100 sample points were randomly distributed within these images and compared the selective logging classification based on Landsat-8 image 232/66.

Finally, Kappa coefficient ( Equation 1 ) ( Cohen, 1960 ) and confusion matrixes were estimated for Mato Grosso, Pará, and Rondônia:

k=Ni=1rxiii=1rxi+*x+iN2i=1rxi+*x+i (1)

where: k = Kappa coefficient; N = total number of sampled points; r = number of rows in the error matrix; xii= value of row i and column i; x+i= total value of column i; xi+= total value of row i.

3. RESULTS AND DISCUSSION

3.1. Accuracy analysis

Our results indicate a good accuracy for the selective logging classification technique. Overall, 91%, 93%, and 93% of accuracy classification were estimated for the states of Mato Grosso, Pará, and Rondônia, respectively. These accuracy results are above the 85% minimum threshold used as reference for good accuracy classification ( Pringle et al., 2009 ). Therefore, our results indicated good agreement between selective logging classification and visual observations on the Rapid Eye images and field.

More specifically, 12% of sampled points were omitted and 9.4% of sampled points were commissioned for selectively logged forests. These results indicated that 88.1% of sampled points observed as selective logging were correctly classified by the applied classification technique ( Table 2 ). The Kappa coefficient presented value of 82% for the technique, with good agreement between the image taken as field truth and the selective exploration classification ( Congalton & Green, 2008 ).

Table 2 Accuracy of the selective logging detection technique in the study area spatially located in the state of Mato Grosso in 2014.  

Usage Classes Rapid Eye image Producer Accuracy User Accuracy
Selective logging Other uses Total
Classified image Selective logging 96 10 106 88.1% 91%
Other uses 13 141 154 93% 92%
Total 109 151 260
Omission errors 11.9% 7%
Commission errors 9.4% 8.4%
Overall accuracy 91%

For the state of Pará, it was estimated that 7.4% of selectively logged forests were omitted and 7.4% were committed by the applied classification technique. Based on underestimation (omitted) and overestimation (committed) errors, 92.6% of selectively logged forests were correctly detected and classified ( Table 3 ). Kappa coefficient showed accuracy of 82%, which is considered good agreement between selective logging observed on the reference Rapid Eye images and field and the Landsat image classification ( Congalton & Green, 2008 ).

Table 3 Accuracy of the selective logging classification technique in the study area spatially located in the state of Pará in 2014.  

Usage Classes Rapid Eye image Producer Accuracy User Accuracy
Selective logging Other uses Total
Classified image Selective logging 87 7 94 92.6% 92.6%
Other uses 7 99 106 93% 93%
Total 94 106 200
Omission errors 7.4% 7%
Commission errors 7.4% 7%
Overall accuracy 93%

Sources of omission and commission errors are mainly caused by the spatial resolution (30m) of Landsat imagery used in this study. Each image pixel using this spatial resolution encompasses 900 m2 in the ground, which leads to spectral mixtures by ground features. These spectral mixtures may increase errors of the automatic classification, leading to misclassifications by applying automatic algorithms and visual interpretation. Altogether, it may reduce classification accuracy.

Another factor affecting classification accuracy is the adjustment of maximum and minimum values of the spatial profile of texture images when applying semiautomatic classification to detect log-landing patios. These values are empirically adjusted based on the spectral response of ground features that represent log-landing patios and may lead to misclassification. Intended omission of subtle and more isolated log-landing patios may occur to avoid potential overestimation errors.

Another source of classification errors is related to the acquisition date of Rapid Eye and Landsat imagery used in each study site. Seasonal variation is crucial in the Amazon region and may abruptly change vegetation spectral responses during dry and wet seasons. In addition, remotely sensing images are not always available for specific dates, which is a challenge for comparison of image classifications. Some forested areas classified as selectively logged may be detected on a specific satellite image and may be missing in another image acquired one month earlier or later due to the seasonal variation effect.

Classification accuracy also may be affected by data transformation from continuous field, such as multispectral images, to categorical image (classified), in which class boundaries are defined. Although several surface targets show well-defined borders or edges, there are many cases showing smooth transition edges. Features showing smooth transition edges are commonly affected by categorical classifications, which ultimately affect classification accuracy ( Gopal & Woodcock, 1994 ), as is the case of selectively logged forests in the Amazon region.

Finally, it was observed that 59 of the 100 sampled points within the state of Rondônia were classified as selectively logged forests. Only 1 of the 59 sampled points was incorrectly classified as other land uses, which resulted in omission error of 2% ( Table 4 ). Six sampled points were incorrectly classified as “other uses”, which resulted in commission error of 9.4%. The selective logging accuracy was 98% and Kappa coefficient was 85.3%, which indicate very good classification performance.

Table 4 Accuracy of the selective logging detection technique in the study site spatially located in the state of Rondônia in 2014.  

Usage Classes Rapid Eye image Producer Accuracy User Accuracy
Selective logging
Selective logging Other uses Total
Classified image Selective logging 58 6 64 98% 90.6%
Other uses 1 35 36 85.4% 97%
Total 59 41 100
Omission errors 2% 14.6%
Commission errors 9.4% 3%
Overall accuracy 93%

3.2. Selective logging classification

Our results showed an increase of selective logging and deforestation in the state of Mato Grosso during the period of analysis ( Figures 3 A and 4 A) ( Table 5 ). This increase occurred mostly within Landsat image 226/68. Despite the increase in forests impacted by logging activities, a decrease in anthropogenic activities in the coming years in the study sites is expected. This is mostly like due to the old colonization frontier characteristics in eastern Mato Grosso where high-intensity selective logging (“logging boom”) activities are commonly followed by timber exhaustion or collapse of native forests ( Keller et al., 2002 ; Veríssimo & Cochrane, 2003 ; Weinhold et al., 2015 ).

Figure 3 Selective logging area detected within the study areas in the states of Mato Grosso (A), Pará (B), and Rondônia (C) in 2003, 2006, 2010, and 2014.  

Figure 4 Selectively logged and deforested areas within the studied sites in the states of Mato Grosso (A), Pará (B) and Rondônia (C) in 2003, 2006, 2010, and 2014.  

Table 5 Selective logging area for Landsat images between 2003 and 2014. 

State Landsat Images Year
2003 2006 2010 2014
Mato Grosso 226/68 4,900.60 5,191.70 3,508.10 6,180.40
226/69 1,220.40 1,394.50 1,067.20 613.4
Pará 223/62 4,030.20 3,660.00 4,868.10 2,354.10
223/63 4,308.60 3,208.80 3,500.80 1,623.90
Rondônia 232/66 43.5 209.4 470 1,745.10

Reduction of selective logging areas and increase of deforestation areas were observed during the period of analysis ( Figures 3 B and 4 B) in the state of Pará. This result is due to the overexploitation of native forests and deforestation, where the boom logging period was over and the area is currently facing the “bust” period, predominantly occupied by deforested lands and, as result, selective logging activities are moved to other areas ( Schneider et al., 2002 ; Weinhold et al., 2015 ). In the area in the state of Rondônia, an increase in the selective logging area during the study period was observed ( Figure 3 C).

In the study area in Rondônia, an increase in the selective logging area was observed ( Figure 4 C), which determined a new selective logging frontier. This new logging frontier, spatially located in Northern Rondônia, is currently experiencing a boom logging period and it is expected to increase in the coming years.

Most processes of forest degradation by selective logging in the Amazon follow the same spatial patterns observed in this study: high commercial value tree species are removed damaging several other trees during the removal process. Selective logging activities remain until most of valuable timber species disappear and land has more value with agriculture or pasture than with forest itself. Ultimately, economically impoverished forests will lead to forest conversion into agricultural fields or pasture lands ( Gerwing et al., 1996 ; Schneider et al., 2002 ; Asner et al., 2006 ).

Meanwhile, depletion of timber resources in some regions (Eastern Pará, Mid-Northern Mato Grosso and Southeastern Rondônia) leads to an increase of agriculture-based land use in the Amazon, mainly the expansion of soybean cropping fields ( Schneider et al., 2002 ; Veríssimo & Cochrane, 2003 ; Tritsch & Arvor, 2016 ; Costa et al., 2017 ) and pastures. Selective logging frontiers are followed by the expansion of agricultural activities. Illegal selective logging has severely degraded natural forest resources in previously known “selective logging centers”. Currently, selective logging is moving towards the state of Amazonas and Western and Northern Pará, often within indigenous and protected areas ( Schneider et al., 2002 ).

4. CONCLUSIONS

The selective logging detection technique that combines visual interpretation and semi-automatic technique based on texture algorithm has shown good classification performance as indicated by the overall accuracy and Kappa coefficient results. Based on results, it could be concluded that this classification technique can be extrapolated for mapping selective logging in other regions of the Brazilian Amazon.

However, image choice for classification and validation should focus on acquisition dates during dry season with higher vegetative stress. By combining vegetation stress due to water deficit and impacts by selective logging activities will enhance selectively logged forests in contrast to undisturbed ones through satellite images. Additionally, impacts by selective logging remain detectable on Landsat images from 1 to 3 years and, therefore, closer proximity image acquisition dates will favor detection techniques.

The results of this study indicated a decrease in selective logged sites in the state of Pará, while the amount of deforested areas increased. In this case, there was a displacement of selective logging activities to new frontiers due to the lack of forests in older colonization regions due to deforestation and conventional and predatory selective logging activities.

Selective logging area in the study sites corresponds to a small portion of the three states of the Brazilian Legal Amazon. Therefore, a broader understanding of the land use dynamics, especially forest impacts, will require more spatially and temporally comprehensive studies.

ACKNOWLEDGEMENTS

This work was supported by the Graduate Program in Forest Science of UnB. We would like to thank the anonymous reviewers of the FLORAM Journal for helping to improve the scientific quality of this article.

FINANCIAL SUPPORT Financial support for this study was provided by Coordination for the Improvement of Higher Education Personnel (CAPES) and by the Brazilian National Council of Science and Technology (CNPQ).

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Received: August 18, 2017; Accepted: November 08, 2017

Eraldo Aparecido Trondoli Matricardi Faculdade de Tecnologia, Universidade de Brasília – UnB, Campus Darcy Ribeiro, Asa Norte, CEP 70910-900, Brasília, DF, Brasil e- mail: ematricardi@gmail.com

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