Automatic River Planform Recognition Tested on Chilean Rivers
Abstract
:1. Introduction
2. Methodology
2.1. Ability to Deal with Rivers with Highly Variable AC Width
2.2. Improvement of Some Indicators and Value Functions (VF)
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- Adjustments or refinement of Value Functions (definition, attributes, and their parameter values);
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- Determination of sinuosity;
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- Constrained sinuosity conditions;
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- Adoption of multiplicative scalar Value Functions (VFs).
2.3. Introduction of the Holistic Categorical Tool Paired with the Planform Tool
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- Identify the discontinuities of Planform type (output of Planform);
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- Then, proceed from the upstream toward the downstream while considering each generic slice i.
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- It determines the “distance of constancy D(i)”; i.e., the number of slices along which the previous type (now changed) were kept constant within half of the significant length centered in the current slice; this distance, by construction, progressively reduces while moving to slices ahead of a discontinuity.
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- “prevailing type K steps forward window”: the algorithm here identifies the most frequent type occurring within the K slices ahead.
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- “prevailing type in the D residual forward window “: analogous task, but in a reduced window of just K − D(i) − 1 slices ahead: this is a moving window ahead within a K horizon, the start of which is anchored to the previous discontinuity (it is changed when the algorithm processes the next discontinuity) and that progressively becomes shorter. Its purpose is to consider which value is prevailing in the vicinity in front of the current slice and so avoid it while concluding that a certain type is prevailing in the K window ahead when it indeed is, but leaving “a hole” (i.e., different types are present) in the most proximal slices:
- When the prevailing type in this window is the same than before the (last) discontinuity → current type was a “local hole” and therefore the previous value is maintained instead;
- When it is “not detectable”, it is maintained;
- Otherwise, the prevailing type within the K forward window is adopted.
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- It identifies discontinuities in the sequence of types just determined by the Holistic I round;
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- Where there is no discontinuity, it maintains the already-computed value;
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- Where there is a discontinuity, if the distance D(i) from the last discontinuity is D(i) < K, it adopts the value type occurring upstream of the discontinuity; otherwise, it maintains the current one.
3. Case Study
3.1. Study Area
3.2. Data and Methods
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- ID of the slice or DGO (i);
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- Length of discretization slice (all slices equal; 50 m was adopted for the three rivers);
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- Length LH(j) of the Hubert segment j(i) corresponding to slice i (several slices were associated with the same segment j); reference moving window length L(i) = f ∗ LH(j(i)), over which the reference width w(j(i)) was calculated, with f inflation factor (f ≥ 1) → corresponding significant length (smoothed) LS(i) = K ∗ w(j(i)) with K characteristic parameter. Notice hence that w(j(i)) in general did not coincide with the local slice width w(i), which could be much more variable along the river: w(j(i)) is a filtered out relative of w(i);
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- AC envelope area (or width);
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- VB area (or width);
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- Area of left, right, and point bank attached bars; area of mid-channel bars;
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- Number of active channels;
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- Max, min, average width of low-flow water channel;
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- Max and average distance between two low-flow channels (when multi-channel);
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- Max whole length of water channel crossing slice i (from its departure from main channel until its joining downstream);
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- Area of wetlands within the VB (for slice i);
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- Sinuosity of reach in which slice i falls (see discussion above on sinuosity iteration).
4. Results and Discussion
4.1. Duqueco River
4.2. Laja River
4.3. Biobío River
4.4. General Considerations
5. Conclusions
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- The ability to characterize large river networks;
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- The possibility of carrying out a regular, systematic monitoring of a river network to detect possible typological changes as clear indicators of (natural or anthropogenic) alterations that have occurred.
Author Contributions
Funding
Data Availability Statement
Acknowledgments
Conflicts of Interest
References
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N | River | Year | L (km) | wmax (m) | wmin (m) | A. Basin (km2) | Qav (m3/s) | N. Macrosegments |
---|---|---|---|---|---|---|---|---|
1 | Duqueco | 2009 | 102 | 634 | 11 | 1551 | 55 | 4 |
2 | Laja | 2019 | 140 | 44 | 5 | 4667 | 151 | 5 |
3 | Biobío | 2020 | 198 (*) | 2649 | 15 | 24,273 | 984 | 5 |
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Nardini, A.G.C.; Salas, F.; Carrasco, Z.; Valenzuela, N.; Rojas, R.; Vargas-Baecheler, J.; Yépez, S. Automatic River Planform Recognition Tested on Chilean Rivers. Water 2023, 15, 2539. https://doi.org/10.3390/w15142539
Nardini AGC, Salas F, Carrasco Z, Valenzuela N, Rojas R, Vargas-Baecheler J, Yépez S. Automatic River Planform Recognition Tested on Chilean Rivers. Water. 2023; 15(14):2539. https://doi.org/10.3390/w15142539
Chicago/Turabian StyleNardini, Andrea Gianni Cristoforo, Francisca Salas, Zoila Carrasco, Noelia Valenzuela, Renzo Rojas, José Vargas-Baecheler, and Santiago Yépez. 2023. "Automatic River Planform Recognition Tested on Chilean Rivers" Water 15, no. 14: 2539. https://doi.org/10.3390/w15142539
APA StyleNardini, A. G. C., Salas, F., Carrasco, Z., Valenzuela, N., Rojas, R., Vargas-Baecheler, J., & Yépez, S. (2023). Automatic River Planform Recognition Tested on Chilean Rivers. Water, 15(14), 2539. https://doi.org/10.3390/w15142539