Note. This work is a part of Rémi Dupas' PhD thesis (in Environment Sciences). I was not directly involved in the supervision of Rémi's PhD thesis.
In this section, we present a method that uses Dynamic Time Warping (DTW) on multimodal time series, i.e. time series that are made of several features recorded over time. The method relies on the assumption that one of the considered modalities (called reference modality in the following) can be used as a reference to (temporally) realign other modalities (Dupas et al., 2015). It has been used in the context of hydrological measurements to align pollutant concentration profiles based on discharge time series.
This approach can be seen as the DTW counterpart of other works that rely on Optimal Transport for Domain Adaptation (Courty, Flamary, Tuia, & Rakotomamonjy, 2017). One significant difference, however, is that it relies on a reference modality for alignment. This design choice is guided by our application context.
Motivating Use Case
Phosphorus (P) transfer during storm events represents a significant part of annual P loads in streams and contributes to eutrophication in downstream water bodies. To improve understanding of P storm dynamics, automated or semi-automated methods are needed to extract meaningful information from ever-growing water quality measurement datasets.
Clustering techniques have proven useful for identifying seasonal storm patterns and thus for increasing knowledge about seasonal variability in storm export mechanisms (e.g., (Aubert et al., 2013)). Clustering techniques usually require calculating distances between pairs of comparable points in multiple time series. For this reason, direct clustering (without using hysteresis-descriptor variables) of high-frequency storm concentration time series is usually irrelevant because the lengths of recorded time series (number of measurement points) might differ and/or measurement points may have different positions relative to the hydrograph (flow rise and recession); hence, it is difficult to calculate a distance between pairs of comparable points.
The aim of this study was to develop a clustering method that overcomes this limit and test its ability to compare seasonal variability of P storm dynamics in two headwater watersheds. Both watersheds are ca. 5 km², have similar climate and geology, but differ in land use and P pressure intensity.
Alignment-based Resampling Method
In the above-described setting, we have access to one modality (discharge, commonly denoted Q) that is representative of the evolution of the flood. Temporal realignment based on this modality allows to overcome three difficulties that can arise when comparing storm-event data. Indeed, time series can have
- different starting times due to the discharge threshold at which the samplers were triggered,
- different lengths, and
- differences in phase that yield different temporal localizations of the discharge peak.
To align time series, we use the path associated with DTW. This matching path can be viewed as the optimal way to perform point-wise alignment of time series.
For each discharge time series x(i)Q, we compute the matching path πQ and use it to find the optimal alignment wrt. the same reference discharge time series xrefQ. The reference discharge time series used in this study is chosen as a storm event with full coverage of flow rise and flow recession phases. Alternatively, one could choose a synthetic idealized storm hydrograph.
We then use barycentric mapping based on the obtained matches to realign other modalities to the timestamps of the reference time series, as shown in the following Figures:
from tslearn.metrics import dtw_path
x_q_ref = to_time_series(
[0.13991821, 0.16294979, 0.31514145, 0.54636252, 0.69737061, 0.87776431,
0.95917049, 0.99667355, 0.98113988, 0.87307521, 0.70341944, 0.59648599,
0.51890249, 0.43674822, 0.38792677, 0.36107532, 0.32893154, 0.30836181,
0.30146932, 0.27417169]
)
x_prime_q = to_time_series(
[0.12127299, 0.12750528, 0.14748864, 0.17853797, 0.2815324 , 0.3848446,
0.51661235, 0.6876372 , 0.83539414, 0.96088103, 1. , 0.82093283,
0.70602368, 0.56334187, 0.47268893, 0.41283418, 0.3747808 , 0.34633213,
0.32026957, 0.30550197]
)
x_prime_srp = to_time_series(
[0.26215067, 0.14032423, 0.07405513, 0.08556629, 0.07101746, 0.0891955 ,
0.22119012, 0.32734859, 0.41433779, 0.43256379, 0.56561361, 0.81348724,
0.93016563, 0.92843896, 0.71375583, 0.55979408, 0.43102897, 0.32704483,
0.27554838, 0.26154313]
)
path, dist = dtw_path(x_prime_q, x_q_ref)
# The resampling happens here:
list_indices = [[ii for (ii, jj) in path if jj == j]
for j in range(len(x_q_ref))]
x_prime_q_resample = to_time_series(
[x_prime_q[indices].mean(axis=0) for indices in list_indices]
)
x_prime_srp_resample = to_time_series(
[x_prime_srp[indices].mean(axis=0) for indices in list_indices]
)
plot_matches(x_prime_q, x_q_ref, x_prime_q_resample, path)
At this point, each time series is transformed to series of n p-dimensional measurements, where n is the length of the reference discharge time series and p is the number of water quality parameters considered in the study (i.e. all modalities except the discharge). In a second step, a standard k-means algorithm is used to cluster realigned time series. Note that a Euclidean distance can be used for clustering since time series have already been temporally realigned; hence, time-sensitive metrics (such as DTW) are no longer needed.
This method proved useful to extract meaningful clusters and an a posteriori analysis of the clusters enabled to identify the export dynamics of pollutants in different geographical areas of the study sites, which then led to management recommendations, as detailed in (Dupas et al., 2015).
References
- Dupas, R., Tavenard, R., Fovet, O., Gilliet, N., Grimaldi, C., & Gascuel-Odoux, C. (2015). Identifying seasonal patterns of phosphorus storm dynamics with dynamic time warping. Water Resources Research, 51(11), 8868–8882. https://doi.org/10.1002/2015WR017338
- Courty, N., Flamary, R., Tuia, D., & Rakotomamonjy, A. (2017). Optimal Transport for Domain Adaptation. IEEE Transactions on Pattern Analysis and Machine Intelligence.
- Aubert, A., Tavenard, R., Emonet, R., De Lavenne, A., Malinowski, S., Guyet, T., … Gascuel-Odoux, C. (2013). Clustering Flood Events from Water Quality Time-Series using Latent Dirichlet Allocation Model. Water Resources Research, 49(12), 8187–8199. https://doi.org/10.1002/2013WR014086