single-tree forest inventory using lidar and aerial images for 3d treetop positioning, species...

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SINGLE-TREE FOREST INVENTORY USING LIDAR AND AERIAL IMAGES FOR 3D TREETOP POSITIONING, SPECIES RECOGNITION, HEIGHT AND CROWN WIDTH ESTIMATION Ilkka Korpela University of Helsinki I. Korpela, B. Dahlin, H. Schäfer, E. Bruun, F. Haapaniemi, J. Honkasalo, S. Ilvesniemi, V. Kuutti, M. Linkosalmi, J. Mustonen, M. Salo, O. Suomi, H. Virtanen

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SINGLE-TREE FOREST INVENTORY USING LIDAR AND AERIAL IMAGES FOR 3D TREETOP POSITIONING, SPECIES RECOGNITION, HEIGHT AND CROWN WIDTH ESTIMATION

Ilkka KorpelaUniversity of Helsinki

I. Korpela, B. Dahlin, H. Schäfer, E. Bruun, F. Haapaniemi, J. Honkasalo, S. Ilvesniemi, V. Kuutti, M. Linkosalmi, J. Mustonen, M. Salo, O. Suomi, H. Virtanen

Contents

Study objectives

Methods – the STRS system

Experimental STRS-based forest Inventory: Data, Field work, Results

Conclusions

Study objectives

Method development and testing in Single-Tree Remote Sensing, STRS

Rationales: Forest inventory, 3D models, Landscape planning

STRS-tasks:- 2D/3D positioning- Species recognition- Height estimation- Crown dimensions Stem diameter, volume, bucking

Single-Tree Remote Sensing, STRS - Revised

• Airborne, active and passive instruments, 2D or 3D• Direct estimation + indirect an allometric estimation phase

• Restrictions: tree discernibility, detectable object size, occlusion and shading, interlaced crowns → ILL-POSED• Alternative or complement to field methods and area-based methods• Accuracy restricted by “allometric noise” → tree and stand- level allometric bias, and tree-level imprecision, dbh ~ 10%.

• Measurements are subject to bias and imprecision• Timber quality remains unsolved, only quantity• Unsolved issues: Species recognition?

Methods – the STRS system we used

• Solves all of the STRS tasks

• Semi-automatic solutions combined with “operator intervention”

• Optional input: 1) images + DTM 2) images + LiDAR + DTM

• Assumptions: large-scale images, semi-dense LiDAR, accurate DTM

• Combine use of images and LiDAR for optimal results

• Constrain and filter using allometric regularities

Methods 1: Multi-scale template matching in 3D treetop positioning

Assume that the optical properties and the shape of trees are invariant to their size.

Maxima at different scales, take global → (X,Y,Z) Treetop

Methods 2: Multi-scale Template matching – Crown width estimation in images

Near-nadir views have been found best for the manual measurement of crown width in aerial images

Methods 3: Species recognition

Spectral valuesTexture

Variation in

- Phenology- Tree age and vigor- Image-object-sun geometry=> reliable automation problematic => bottleneck in STRS

Methods 4: LS-adjustment of a crown model with LiDAR points

Assume that

1) Photogrammetric 3D treetop position is accurate

2) Trees have no slant

3) Crowns are ± rotation symmetric

4) We know tree height and species approximation of crown size and shape

→ LiDAR hits are “observations of crown radius at a certain height below the apex”

Assume a rather large crown and collectLiDAR hits in the vicinity of the 3D treetop position. Use LS-adjustment to find a crown model.

LiDAR hits are observations of crown radius at a certain height below the apex?

Example - a 22-m high birch:

Solution in six iterations.

Final RMSE 0.47 m

RMSEs have been larger for birch in comparison to pine and spruce.

Methods 5: Allometric estimation of stem diameterand saw/pulp log volumes – stem bucking

iii dcrmbhadbh

Species-specific regression equations that map maximal crown width (dcrm) and tree height (h) into dbh (Kallio virta and Tokola, 2005)

Species-specific polynomial regression equations that model the tapering of stem diameter (Laasasenaho 1982)

Experimental forest inventory – STRS measurements

• 56.8-ha forest. 25-70 and 100-130-yr-old.

• CIR and PAN-RGBIR images with 12 cm and 9 cm GSD

• ALTM3100 LiDAR with 6-9 pulses per m2

• A LiDAR-based DTM

• 5294 STRS-trees in 59 0.04-ha plots. 165 trees/hour with variables

- Treetop position in XYZ - h, photogrammetric - h, LiDAR-based - Sp, photogrammetric - dcrm, photogrammetric - dcrm LiDAR-based

Experimental forest Inventory – FIELD measurements

Before going to the field, process the STRS measurements into maps and tree labels

Experimental forest Inventory – FIELD measurements

1. Find the plot center using satellite positioning and the tree map

2. Find and label the STRS-trees using triangulation with a compass (solve commission errors)

3. Label the unseen trees in the circular 0.04-ha plot (you are left with omission errors)

4. Position in XY the unseen trees with trilateration and triangulation (ref. Silva Fennica 3/07), ~ 0.3 m.

5. Measure the trees for reference values of Sp, dbh and height

RESULTS – Which trees could we observe and position?

- Omission errors: 38.8% in stem number (dbh > 50 mm)- Commission errors ~ 1-2%- Dominating trees were measurable, but not those with fused crowns- Less than 50% of the trees with a relative height of below 0.7 were detectable

”Tree discernibility” = proportion (%) of detected trees as a function of relative tree height.

Overall Sp-recognition accuracy was ~ 95%,which is at an acceptable level.

RESULTS – Visual tree species recognition

- Multi-scale TM + LiDAR DTM ~ 0.71 m RMSE, 14-cm underestimation- Highest LiDAR hits + LiDAR DTM ~ 0.82 m RMSE, 58-cm underestimation

Accuracy varied between species. DTM-errors were meaningless.

RESULTS – Height estimation accuracy

Residual plot

RESULTS – DBH estimation accuracy

- Photogrammetric height, species and dcrm 28.7% RMSE with a 20-% underestimation

- Photogrammetric height, species and LiDAR-based dcrm 19.6% RMSE with a 6-% underestimation

Tests were not performed, where the dcrm-measurements had not been used.

RESULTS – Volume estimation accuracy

With the use of images alone, an RMSE of 60% was observed for the single-tree stem volume estimates.

By using LiDAR-based measurements of crown width (dcrm), the RMSE was 46%.

RESULTS – Forest inventory

Omission errors → 10% of total volume missedDBH underestimation by 1 cm → underest. of total and saw wood volumeDBH-estimates were averaged → skew in saw/pulp wood proportions

Conclusions

The system worked partly well, and it solved all of the STRS-tasks, and provided results per species and timber sortiment, but

- Results of timber resources were contaminated by large systematic errors and noise due to measurement errors and model errors (averaging)

Calibration of measurements and model estimates is needed, also a better allometric DBH-estimation phase

- Many of the tasks need a more automatic solution, especially the Sp-recognition task.