Extraction of Visible Boundaries for Cadastral Mapping Based on UAV Imagery
Abstract
:1. Introduction
1.1. Visible Boundary Detection and Extraction for Cadastral Mapping
1.2. Objective of the Study
2. Materials and Methods
2.1. UAV Data
2.2. Reference data
2.3. Visible Boundary Delineation Method and Workflow
2.3.1. ENVI Feature Extraction (FX)
2.3.2. Visible Boundary Delineation Workflow
- Image pre-processing: The first step is resampling the UAV orthoimage. The UAV orthoimage was resampled from 2 cm to lower spatial resolutions—25 cm, 50 cm and 100 cm ground sample distances (GSD). The selected GSDs allowed the identification of the impact of different GSDs on the results of automatic boundary extractions. The pixel average method was used for resampling the UAV orthoimage as it provides a smoother image. In addition, further resampling methods (nearest neighbor and bilinear) were tested and did not provide significant differences in the number of automatic object boundary extractions—at higher scale and merge levels of the ENVI FX algorithm. The resampling step was also applied in [26], to make transferable the investigated method to a UAV orthoimage for cadastral mapping purposes. In addition, extracting objects from a UAV orthoimage of lower spatial resolution is computationally less expensive.
- Boundary detection and extraction: The ENVI FX module was applied to each down-sampled UAV orthoimage. The detection and extraction of visible boundaries from the UAV orthoimage was based on the ENVI FX scale and merge level values. The texture kernel size was set to default, i.e., 3. In addition, further object extractions were tested at the highest texture kernel size and no differences in the number and locations of extracted objects were identified. Scale level values ranged from 50 to 80 and merge level values from 50 to 99. The initial incremental value for both scale and merge levels was 10. In cases where a jump in the total number of extracted objects was detected the incremental value was dropped for both scale and merge levels. In order to identify the optimal scale and merge values for the detection and extraction of visible objects for cadastral mapping, all possible range values of scale and merge combinations were tested. For each extraction information about the total number of extracted objects and processing time was stored. This resulted in 50 boundary maps for each resampled UAV orthoimage. The boundary map consisted of extracted objects (polygon-based), which were in digital vector format.
- Data post-processing: The process included two steps: (i) the filtering of extracted objects, and (ii) the simplification of extracted objects. (i) The minimum object area and the total number of objects identified in the reference data (Figure 1b) were used to determine optimal scale and merge levels. The minimum reference object area was 204 m2, and the total number of objects was 68. All extracted objects that were smaller than the minimum object area from reference data were filtered out (removed). The total number of remaining objects was compared with the total number of objects from the reference data and the tolerance of +/- 10 objects was set—those parameters that produced numbers of objects that were closest to those found in the reference data, i.e., within defined tolerance, were deemed optimal. The boundary maps from which smaller objects were removed were labeled as filtered objects. The output of filtered objects consisted of holes, i.e., due to polygon-based geometry of objects, which were mostly present either in the forest or individual trees and are of less relevance for cadastral applications—a boundary between adjacent objects belongs to both. (ii) Extracted and filtered object boundaries were smoothed and simplified to be used for the interpretation of possession boundaries aiming to support a cadastral mapping (i.e., land plot restructuring in this case, as the situation requires a new cadastral survey or land consolidation). The smoothing of extracted/filtered object boundaries was done by using the Snakes algorithm [49]. The Douglas–Peucker algorithm was applied to the smoothed object boundaries in order to further simplify the object boundaries [22,49]. These objects both smoothed and simplified were labeled as simplified extracted/filtered objects.
- Accuracy assessment: The accuracy assessment was object-based since the results were in vector format. The buffer overlay method was used for accuracy assessment. The method is described in detail in Heipke et al. [50]. The accuracy assessment was based on computing the percentages of extracted (or reference) boundary lengths which overlapped within a buffer polygon area generated around the reference (or extracted) boundaries (Figure 3) [50]. To determine the completeness, correctness, and quality of extracted boundaries, calculated boundary lengths of true positives (TP), false positives (FP), and false negatives (FN) were used. The completeness refers to the percentage of reference boundaries which lie within the buffer around the extracted boundaries (matched reference). The correctness refers to the percentage of extracted boundaries, which lie within the buffer around the reference boundaries (matched extraction). The accuracy assessment was performed on buffer widths of 25 cm, 50 cm, 100 cm, and 200 cm. The selection of buffer widths is in line with other studies and was based on the most common tolerances regarding boundary positions in land administration, especially for rural areas [26,27]. The percentage indicating the overall quality was generated from the previous two by dividing the length of the matched extractions with the sum of the length of extracted data and the length of unmatched reference [50]. The accuracy assessment was applied to automatic extracted objects, simplified extracted objects, filtered objects, and simplified filtered objects (Figure 2).
3. Results
4. Discussion
4.1. The Developed Workflow
4.2. Quality Assessment
4.3. Strengths and Limitations of the Automatic Extraction Method Used
4.4. Applicability of the Developed Workflow
5. Conclusions
Author Contributions
Funding
Acknowledgments
Conflicts of Interest
Abbreviations
DSM | Digital Surface Model |
ESP | Estimation of Scale Parameter |
FIG | International Federation of Surveyors |
FN | False Negative |
FP | False Positive |
FX | ENVI Feature Extraction |
GCP | Ground Control Point |
GIS | Geographic Information System |
GNSS | Global Navigation Satellite System |
gPb | Global Probability of Boundary |
GSD | Ground Sample Distance |
HRSI | High-Resolution Satellite Imagery |
MRS | Multi-Resolution Segmentation |
PDOP | Position Dilution of Precision |
RMSE | Root-Mean-Square-Error |
RTK | Real-Time Kinematic |
SLIC | Simple Linear Iterative Clustering |
TP | True Positive |
UAV | Unmanned Aerial Vehicle |
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Location | UAV Model | Camera/Focal Length [mm] | Overlap Forward/Sideward [%] | Flight altitude [m] | GSD [cm] | Pixels |
---|---|---|---|---|---|---|
Ponova vas, Slovenia | DJI Phantom 4 Pro | 1” CMOS 20mp/24 | 80/70 | 80 | 2.0 | 35,551 × 31,098 |
GSD [cm] | Pixels | Resampling Method |
---|---|---|
25 | 2856 × 2498 | Pixel average |
50 | 1428 × 1249 | Pixel average |
100 | 714 × 625 | Pixel average |
Buffer width [cm] | Completeness [%] | Correctness [%] | Quality [%] | |||
---|---|---|---|---|---|---|
Extracted | Filtered | Extracted | Filtered | Extracted | Filtered | |
25 | 58 | 37 | 18 | 26 | 16 | 20 |
50 | 73 | 48 | 28 | 39 | 26 | 31 |
100 | 78 | 56 | 38 | 50 | 36 | 41 |
200 | 81 (81) 1 | 61 (62) 1 | 48 (49) 1 | 59 (61) 1 | 46 (46) 1 | 50 (48) 1 |
Buffer width [cm] | Completeness [%] | Correctness [%] | Quality [%] | |||
---|---|---|---|---|---|---|
Extracted | Filtered | Extracted | Filtered | Extracted | Filtered | |
25 | 45 | 40 | 28 | 35 | 21 | 23 |
50 | 64 | 55 | 46 | 56 | 38 | 41 |
100 | 71 | 61 | 57 | 68 | 48 | 52 |
200 | 75 (74) 1 | 65 (67) 1 | 65 (66) 1 | 76 (77) 1 | 56 (53) 1 | 59 (56) 1 |
Buffer Width [cm] | Completeness [%] | Correctness [%] | Quality [%] | |||
---|---|---|---|---|---|---|
Extracted | Filtered | Extracted | Filtered | Extracted | Filtered | |
25 | 31 | 27 | 21 | 24 | 14 | 15 |
50 | 53 | 47 | 39 | 43 | 29 | 30 |
100 | 67 | 59 | 58 | 64 | 47 | 47 |
200 | 73 (71) 1 | 63 (67) 1 | 66 (66) 1 | 72 (73) 1 | 55 (52) 1 | 55 (52) 1 |
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Fetai, B.; Oštir, K.; Kosmatin Fras, M.; Lisec, A. Extraction of Visible Boundaries for Cadastral Mapping Based on UAV Imagery. Remote Sens. 2019, 11, 1510. https://doi.org/10.3390/rs11131510
Fetai B, Oštir K, Kosmatin Fras M, Lisec A. Extraction of Visible Boundaries for Cadastral Mapping Based on UAV Imagery. Remote Sensing. 2019; 11(13):1510. https://doi.org/10.3390/rs11131510
Chicago/Turabian StyleFetai, Bujar, Krištof Oštir, Mojca Kosmatin Fras, and Anka Lisec. 2019. "Extraction of Visible Boundaries for Cadastral Mapping Based on UAV Imagery" Remote Sensing 11, no. 13: 1510. https://doi.org/10.3390/rs11131510
APA StyleFetai, B., Oštir, K., Kosmatin Fras, M., & Lisec, A. (2019). Extraction of Visible Boundaries for Cadastral Mapping Based on UAV Imagery. Remote Sensing, 11(13), 1510. https://doi.org/10.3390/rs11131510